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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.
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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
R007XY014OR Loamy 8-10 PZ
Loamy 8-10" PZ
R007XY013OR Sandy Loam 8-10 PZ
Sandy Loam 8-10" PZ
R007XY015OR Shallow Loam 8-10 PZ
Shallow Loam 8-10" PZ
Similar sites
R007XY014OR Loamy 8-10 PZ
Loamy 8-10" PZ (less steep, not as droughty)
R007XY015OR Shallow Loam 8-10 PZ
Shallow Loam 8-10" PZ (shallow soils)
R007XY013OR Sandy Loam 8-10 PZ
Sandy Loam 8-10" PZ (less steep, not as droughty)
Table 1. Dominant plant species
Tree Not specified
Shrub Not specified
Herbaceous Not specified
Physiographic features
This site occurs on side slopes of hills and dissected plateaus on mostly southerly aspects.
Table 2. Representative physiographic features
Landforms (1) Hill
(2) Plateau
Flooding frequency None Elevation 500 – 1200 ft Slope 12 – 40 % Water table depth 72 in Aspect SE, S, SW Climatic features
The annual precipitation ranges form 8 to 10 inches which occurs mostly as rain during the months of November through April. The temperature regime is mesic with extremes ranging from 115 degrees F to -10 degrees F. The frost-free period is 200 to 230 days and the optimum period for plant growth is early March through mid-May.
Table 3 Representative climatic features
Frost-free period (average) 230 days Freeze-free period (average) Precipitation total (average) 10 in ">Influencing water features
Soil features
The soils of this site are moderately deep to very deep, well drained fine sandy loams to gravelly silt loams. They are formed over alluvium, loess, or lacustrine sediments. Permeability is moderately rapid and reaction is neutral to moderately alkaline in the subsoils. Runoff is low and the erosion hazard is moderate for both water and wind.
Table 4. Representative soil features
Surface texture (1) Fine sandy loam
(2) Gravelly silt loam
Family particle size (1) Loamy
Drainage class Well drained Permeability class Moderately rapid Soil depth 60 in Ecological dynamics
If heavy grazing causes site deterioration, broom snakeweed and gray rabbitbrush will strongly increase along with big sagebrush. Annuals like cheatgrass, mustard, russian thistle, and china lettuce readily invade the site.
Variation in plant composition on this site results from variations in soil surface texture. Fine textured surfaces favor the establishment of bluebunch wheatgrass. Coarse textured surfaces will encourage a higher proportion of needleandthread. Gravels increase the proportion of Thurber needlegrass.State and transition model
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Click on state and transition labels to scroll to the respective textEcosystem states
State 1 submodel, plant communities
State 1
ReferenceCommunity 1.1
Bluebunch Wheatgrass, Needle and Thread, and Sandberg BluegrassVariation in plant composition on this site results from variations in soil durface texture. Fine textured surfaces (silts) favor the establishment of bluebunch wheatgrass. Coarse textured surfaces (fine sands) will encourage a higher percentage of needle and thread. Gravels increase the proportion of thurber needlegrass.
Figure 2. Annual production by plant type (representative values) or group (midpoint values)
Table 5. Annual production by plant type
Plant type Low
(lb/acre)Representative value
(lb/acre)High
(lb/acre)Grass/Grasslike 272 380 484 Forb 20 40 60 Shrub/Vine 12 20 28 Total 304 440 572 Figure 3. Plant community growth curve (percent production by month). OR2271 , B7 LOAMY, GOOD CONDITION. RPC growth curve B7 LOAMY, GOOD CONDITION.
Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec J F M A M J J A S O N D 0 15 25 20 15 10 0 0 5 10 0 0 Additional community tables
Table 6. Community 1.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Grass/Grasslike1 Dominant deep rooted perennial grasses 200–280 bluebunch wheatgrass PSSP6 Pseudoroegneria spicata 200–280 – 2 Sub-dominant deep rooted perennial grasses 44–132 needle and thread HECO26 Hesperostipa comata 40–120 – Thurber's needlegrass ACTH7 Achnatherum thurberianum 4–12 – 3 Dominant shallow rooted perennial grasses 20–60 Sandberg bluegrass POSE Poa secunda 20–60 – 5 Other perennial grasses 8–12 Indian ricegrass ACHY Achnatherum hymenoides 0–8 – squirreltail ELEL5 Elymus elymoides 0–8 – Forb7 Dominant perennial forbs 16–48 balsamroot BALSA Balsamorhiza 4–12 – buckwheat ERIOG Eriogonum 4–12 – desertparsley LOMAT Lomatium 4–12 – phlox PHLOX Phlox 4–12 – 9 Other perennial forbs 4–12 common yarrow ACMI2 Achillea millefolium 0–4 – milkvetch ASTRA Astragalus 0–4 – lupine LUPIN Lupinus 0–4 – Shrub/Vine11 Dominant evergreen shrubs 4–12 basin big sagebrush ARTRT Artemisia tridentata ssp. tridentata 4–12 – 12 Sub-dominant evergreen shrubs 4–8 rubber rabbitbrush ERNA10 Ericameria nauseosa 4–8 – 15 Other shrubs 4–8 Wyoming big sagebrush ARTRW8 Artemisia tridentata ssp. wyomingensis 0–4 – broom snakeweed GUSA2 Gutierrezia sarothrae 0–4 – Interpretations
Animal community
This site provides food and cover for sondbirds, small mammals and their associated predators. It can also provide part of the winter-early spring diet for mule deer and antelope.
The scarcity of water is the limiting factor in the use of this site by wildlife. When located near water it furnishes valuable winter-early spring feed to deer and antelope.
Livestock Grazing:
Because of its southerly exposure and warmer soil temperatures, this site is commonly the first to show plant growth. These factors contribute to rapid soil moisture depletion, therefore special consideration is required in grazing management to allow for plant regrowth.Hydrological functions
The soils of this site have moderate intake rates and high runoff potential. The hydrologic soil group is B.
Other information
Caution must be exercised in developing a seeding plan because the soils are droughty and subject to moderate to severe wind erosion.
Supporting information
Contributors
Alan Bahn
E Ersch (OSU)
JPRApproval
Kirt Walstad, 2/06/2025
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 NRCS State Rangeland Management Specialist Date 07/26/2012 Approved by Approval date Composition (Indicators 10 and 12) based on Annual Production Indicators
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Number and extent of rills:
Few, moderate sheet & rill erosion hazard -
Presence of water flow patterns:
Few to many, depending on slope and plant cover -
Number and height of erosional pedestals or terracettes:
None -
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
2-10% -
Number of gullies and erosion associated with gullies:
None -
Extent of wind scoured, blowouts and/or depositional areas:
Very few possible, moderate to severe 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):
Moderatley to slightly resistant to erosion; aggregate stability = 3-4 -
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
Moderately deep to very deep, well drained, fine sandy loams to gravelly silt loams; low OM (1-2%) -
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
Moderate ground cover (30-50%) should limit rainfall impact and overland flow on lower slopes (12-20%); increased flow likely on steeper slopes (up to 40%) -
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 > Needle and thread > Sandberg bluegrass > Thurber needlegrass = other grasses = dominant forbs = other forbs = Basin big sagebrush >= Gray rabbitbrush = other shrubsSub-dominant:
Other:
Additional:
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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):
In areas with adequate plant cover -
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
Favorable: 700, Normal: 400, Unfavorable: 300 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:
Rabbitbrush, sage brush and broom snakeweed may increase and reduce cover of herbaceous plants. Cheatgrass and annual forbs invade sites that have lost shallow rooted perennial grass functional groups -
Perennial plant reproductive capability:
All species should be capable of reproducing annually
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