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Natural Resources
Conservation Service
Ecological site R011XY018OR
Shallow Loam 8-11 PZ
Accessed: 08/17/2024
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.
![Location map](/images/maps/R011XY018OR.png)
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
R011XY012OR |
Silty 8-11 PZ Silty 8-11 PZ |
---|---|
R011XY013OR |
Clayey 8-11 PZ Clayey 8-11 PZ |
R011XY020OR |
South Slopes 8-11 PZ South Slopes 8-11 PZ |
R011XY032OR |
Silty North Slopes 8-11 PZ Silty North Slopes 8-11 PZ |
Similar sites
R011XY012OR |
Silty 8-11 PZ Silty 8-11 PZ (deeper soil, greater production) |
---|---|
R011XY013OR |
Clayey 8-11 PZ Clayey 8-11 PZ (clayey surface, deeper soil, greater production) |
Table 1. Dominant plant species
Tree |
Not specified |
---|---|
Shrub |
(1) Artemisia tridentata ssp. wyomingensis |
Herbaceous |
(1) Achnatherum thurberianum |
Physiographic features
This site occurs on low elevation terraces in the Malheur, Owyhee and adjacent Snake River drainage. Slopes typically range from 0 to 12%. Elevations vary from 2,100 to 3,200 feet.
Table 2. Representative physiographic features
Landforms |
(1)
Terrace
|
---|---|
Elevation | 640 – 975 m |
Slope | 0 – 12% |
Aspect | Aspect is not a significant factor |
Climatic features
The annual precipitation ranges from 8 to 11 inches, most of which occurs in the form of rain during the months of December through April. The soil temperature regime is mesic with a mean air temperature of 53 degrees F. Temperature extremes range from 110 to -10 degrees F. The frost free period ranges from 150 to 190 days. The optimum growth period for plant growth is late March through June.
Table 3. Representative climatic features
Frost-free period (average) | 190 days |
---|---|
Freeze-free period (average) | 0 days |
Precipitation total (average) | 279 mm |
Figure 2. Monthly average minimum and maximum temperature
Influencing water features
Soil features
The soils of this site are typically shallow and well drained. Typically the surface layer is a silt loam to a very fine sandy loam 4 to 8 inches thick. The subsoil is a silt loam to silty clay loam 8 to 12 inches thick. Depth to bedrock or compacted lacustrine and alluvial sediments ranges from 10 to 20 inches. An indurate pan may be present. Permeability is moderate. The available water holding capacity (AWC) is about 2 to 4 inches for the profile. The erosion potential is moderate to severe.
Table 4. Representative soil features
Surface texture |
(1) Silt loam (2) Fine sandy loam |
---|---|
Family particle size |
(1) Loamy |
Drainage class | Well drained to moderately well drained |
Permeability class | Moderate to moderately slow |
Soil depth | 25 – 51 cm |
Available water capacity (0-101.6cm) |
5.08 – 10.16 cm |
Ecological dynamics
The potential native plant community is dominated by Wyoming big sagebrush, spiny hopsage and Thurber’s needlegrass. Beardless wheatgrass is prominent to co-dominant with Thurber's needlegrass. Sandberg bluegrass is the dominant shallow rooted perennial grass. A variety of forbs and shrubs are present. Vegetative composition of the community is approximately 75 percent grasses, 10 percent forbs and 15 percent shrubs. The approximate ground cover is 60 to 70 percent (basal and crown).
Range in Characteristics:
Wyoming big sagebrush and spiny hopsage are co-dominant with Wyoming big sagebrush increasing at the upper end of the precipitation zone and spiny hopsage on droughtier sites. Thurber’s needlegrass increases on very fine sandy loam surfaces, in lower precipitation areas and on droughtier sites. Beardless wheatgrass increases on silty surfaces. Needle and thread is present on coarser surfaces. Sandberg bluegrass occurs in association with a strong microbiotic crust. Winterfat increases in lower precipitation areas on silts. Production increases at the upper end of the precipitation zone.
Response to Disturbance:
When the condition of the site deteriorates as a result of over grazing Thurber’s needlegrass and beardless wheatgrass rapidly decrease. Wyoming big sagebrush, spiny hopsage, squirreltail and Sandberg bluegrass increase. Cheatgrass, other annuals, biennial weeds and bulbous bluegrass invade. With fire and continued disturbance big sagebrush is severely impacted. Rabbitbrush increases slightly and annuals and noxious biennial forbs strongly invade. Bare ground increases and excessive erosion contributes to downstream sedimentation. The excessive erosion is most pronounced in drainage areas where deep incised gulley’s form.
States: ARTRW/POSE-BRTE (degraded without fire); POSE-POBU/biennial forbs and BRTE/biennial forbs (following fire on degraded range)
State and transition model
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Ecosystem states
State 1 submodel, plant communities
State 1
Historic Climax Plant Community
Community 1.1
Historic Climax Plant Community
The potential native plant community is dominated by Wyoming big sagebrush, spiny hopsage and Thurber’s needlegrass. Beardless wheatgrass is prominent to co-dominant with Thurber's needlegrass. Sandberg bluegrass is the dominant shallow rooted perennial grass. A variety of forbs and shrubs are present. Vegetative composition of the community is approximately 75 percent grasses, 10 percent forbs and 15 percent shrubs. The approximate ground cover is 60 to 70 percent (basal and crown).
Figure 3. 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 | 252 | 420 | 673 |
Shrub/Vine | 50 | 84 | 135 |
Forb | 34 | 56 | 90 |
Total | 336 | 560 | 898 |
Additional community tables
Table 6. Community 1.1 plant community composition
Group | Common name | Symbol | Scientific name | Annual production (kg/hectare) | Foliar cover (%) | |
---|---|---|---|---|---|---|
Grass/Grasslike
|
||||||
1 | Dominant, perennial, deep-rooted bunchgrasses | 280–392 | ||||
Thurber's needlegrass | ACTH7 | Achnatherum thurberianum | 168–224 | – | ||
beardless wheatgrass | PSSPI | Pseudoroegneria spicata ssp. inermis | 112–168 | – | ||
4 | Sub-dominant, perennial, shallow-rooted grasss | 17–45 | ||||
Sandberg bluegrass | POSE | Poa secunda | 17–45 | – | ||
5 | Other perennial grasses | 17–73 | ||||
bluebunch wheatgrass | PSSPS | Pseudoroegneria spicata ssp. spicata | 11–28 | – | ||
Indian ricegrass | ACHY | Achnatherum hymenoides | 0–11 | – | ||
squirreltail | ELEL5 | Elymus elymoides | 6–11 | – | ||
needle and thread | HECO26 | Hesperostipa comata | 0–11 | – | ||
foxtail wheatgrass | PSSA2 | ×Pseudelymus saxicola | 0–11 | – | ||
Forb
|
||||||
8 | Sub-dominanat, perennial forbs | 34–67 | ||||
common yarrow | ACMI2 | Achillea millefolium | 6–11 | – | ||
hairy balsamroot | BAHOH | Balsamorhiza hookeri var. hirsuta | 6–11 | – | ||
fleabane | ERIGE2 | Erigeron | 6–11 | – | ||
buckwheat | ERIOG | Eriogonum | 6–11 | – | ||
desertparsley | LOMAT | Lomatium | 6–11 | – | ||
phlox | PHLOX | Phlox | 6–11 | – | ||
9 | Other perennial forbs | 11–62 | ||||
onion | ALLIU | Allium | 2–6 | – | ||
pussytoes | ANTEN | Antennaria | 2–6 | – | ||
milkvetch | ASTRA | Astragalus | 2–6 | – | ||
tapertip hawksbeard | CRAC2 | Crepis acuminata | 2–6 | – | ||
lupine | LUPIN | Lupinus | 2–6 | – | ||
hoary tansyaster | MACA2 | Machaeranthera canescens | 0–3 | – | ||
plains pricklypear | OPPO | Opuntia polyacantha | 0–3 | – | ||
beardtongue | PENST | Penstemon | 0–3 | – | ||
scarlet globemallow | SPCO | Sphaeralcea coccinea | 0–3 | – | ||
deathcamas | ZIGAD | Zigadenus | 0–3 | – | ||
common woolly sunflower | ERLA6 | Eriophyllum lanatum | 0–3 | – | ||
haplopappus | HAPLO11 | Haplopappus | 0–3 | – | ||
woodland-star | LITHO2 | Lithophragma | 0–3 | – | ||
mariposa lily | CALOC | Calochortus | 0–3 | – | ||
bastard toadflax | COMAN | Comandra | 0–3 | – | ||
Shrub/Vine
|
||||||
11 | Dominant shrubs | 45–101 | ||||
spiny hopsage | GRSP | Grayia spinosa | 17–45 | – | ||
15 | Other shrubs | 11–34 | ||||
winterfat | KRLA2 | Krascheninnikovia lanata | 0–7 | – | ||
littleleaf horsebrush | TEGL | Tetradymia glabrata | 3–6 | – | ||
rubber rabbitbrush | ERNA10 | Ericameria nauseosa | 3–6 | – | ||
broom snakeweed | GUSA2 | Gutierrezia sarothrae | 0–6 | – |
Interpretations
Animal community
Livestock Grazing:
This site is suitable for livestock grazing use in the late fall, winter and early spring under a planned grazing system. Use should be postponed until the soils are firm enough to prevent trampling damage and soil compaction. Grazing management should be keyed for Thurber’s needlegrass and beardless wheatgrass. Deferred grazing or rest is recommended at least once every three years.
Native Wildlife Associated with the Potential Climax Community:
This site is commonly used by pronghorn antelope, mule deer, rabbits, rodents, upland birds and various predators. It is a preferred site for sage grouse wintering. Antelope and mule deer make excellent use of the site for winter and early spring forage.
Hydrological functions
The soils of this site are typically in an upland topographic position. They have moderate runoff potential and medium infiltration rates when the hydrologic cover is high. Hydrologic cover is high when the Thurber’s needlegrass and beardless wheatgrass deep rooted bunchgrass component is greater than 70 percent of potential.
Supporting information
Contributors
T.Bloomer, E.Petersen, A.Bahn
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) | Bob Gillaspy |
---|---|
Contact for lead author | State Rangeland Management Specialist for NRCS Oregon |
Date | 11/17/2016 |
Approved by | Bob Gillaspy |
Approval date | |
Composition (Indicators 10 and 12) based on | Annual Production |
Indicators
-
Number and extent of rills:
None, moderate sheet & rill erosion hazard. -
Presence of water flow patterns:
None, except following high intensity storms when short (less than 1 meter) flow patterns may appear on steeper slopes. Minimal evidence of past or current soil deposition or erosion. -
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):
10-30% bare ground. Typically bare patches are associated with shrubs. Larger bare patches maybe associated with ant mounds, rodent, and/or other natural disturbances. -
Number of gullies and erosion associated with gullies:
None. -
Extent of wind scoured, blowouts and/or depositional areas:
None. Wind erosion hazard is slight to moderate. -
Amount of litter movement (describe size and distance expected to travel):
Litter size is Small/Fine. Litter movement is limited, minimal, and short, associated with water flow patterns following extremely high intensity storms. Litter also may be moved during intense wind storms. -
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
Site is Moderately resistant to erosion. Stability class (Herrick et al. 2001) anticipated to be 3-6 at surface under perennial vegetation. Stability class at surface in the interspaces is anticipated to be less than or equal to that under perennial vegetation. -
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
Surface layer structure is weak medium platy. The A horizon has a dry color of 6 and is 8 - 12 inches thick. The Soil Organic Matter (SOM) content is low (0.5 to 2.0%). -
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
Plant foliar cover and basal cover with moderate to large gaps between plants should slightly reduce raindrop impact and slow overland flow, providing some increased time for infiltration to occur. Low herbaceous vegetation on this site will retain some water from precipitation. Low ground cover (50-55%) and gentle slopes (0-12%) slightly to moderately 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:
Deep rooted bunchgrassesSub-dominant:
Evergreen shrubsOther:
Perennial forbs >= shallow rooted bunchgrassesAdditional:
-
Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
Grasses will nearly always show some mortality and decadence. Normal decadence and mortality expected on other plants. -
Average percent litter cover (%) and depth ( in):
-
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
Low 300 lbs/acre, Representative Value 500 lbs/acre, High 700 lbs/acre -
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:
Annuals (Cheatgrass, Medusahead, and forbs) invade sites that have lost deep rooted perennial grass functional groups. -
Perennial plant reproductive capability:
All species should be capable of reproducing annually.
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