Search

Search for a Major Land Resource Area or ecological site by name and/or ID.

Natural Resources
Conservation Service

Ecological site R023XY213OR

SANDY LOAM 10-12 PZ

Accessed: 11/21/2024

Home / Esd catalog / MLRA 023X / Ecological site R023XY213OR

USC

Metric

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.

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

R023XY212OR	LOAMY 10-12 PZ Loamy 10-12" PZ
R023XY300OR	SOUTH SLOPES 10-12 PZ South Slopes 8-12" PZ

R023XY212OR

LOAMY 10-12 PZ

Loamy 10-12" PZ

R023XY300OR

SOUTH SLOPES 10-12 PZ

South Slopes 8-12" PZ

Similar sites

R023XY212OR	LOAMY 10-12 PZ Loamy 10-12" PZ (finer surface texture)

R023XY212OR

LOAMY 10-12 PZ

Loamy 10-12" PZ (finer surface texture)

Table 1. Dominant plant species

Tree	Not specified
Shrub	(1) Artemisia tridentata ssp. tridentata
Herbaceous	(1) Hesperostipa comata (2) Achnatherum thurberianum

Download full description

Physiographic features

This site occurs on plateaus and tablelands. Slopes range from 0 to 15 percent. Elevation varies from 4200 to 5500 feet.

Table 2. Representative physiographic features

Landforms	(1) Plateau
Elevation	4,200 – 5,500 ft
Slope	15%
Water table depth	60 in
Aspect	Aspect is not a significant factor

Climatic features

The annual precipitation ranges from 10 to 12 inches, most of which occurs in the form of snow during the months of December through March. Localized convection storms occasionally occur during the summer. The soil temperature regime is frigid to near frigid with a mean annual air temperature of 47 degrees F. Temperature extremes range from 100 to -30 degrees F. The frost-free period ranges from 50 to 90 days. The optimum growth period for native plants is from mid-April through June.

Table 3. Representative climatic features

Frost-free period (average)	90 days
Freeze-free period (average)	0 days
Precipitation total (average)	12 in

Soil features

The soils of this site are typically moderately deep to deep over a duripan and/or bedrock. The soils have a loamy sand to sandy loam surface texture 10 to 20 inches thick. The surface is often overblown. The subsoil and/or substratum is typically medium to fine-textured. Permeability is moderate to rapid. The available water holding capactiy (AWC) is about 3 to 6 inches for the profile. The potential for wind erosion is moderate to severe.

Table 4. Representative soil features

Surface texture	(1) Loamy sand (2) Sandy loam
Family particle size	(1) Loamy
Drainage class	Well drained
Permeability class	Moderate to rapid
Available water capacity (0-40in)	3 – 6 in

Ecological dynamics

Range in Characteristics:

Variability in plant composition and production results from variation in soil surface texture and depth. Needle-and-thread will increase on a loamy sand surface. Production will increase with soil depth. Thurber needlegrass will increase on shallower soils where the surface texture is finer and the amount of fine gravels in the surface increases. As a fire susceptible site, the amount of basin big sagebrush is dependent on fire frequency.

Response to Disturbance:

If the condition of the site deteriorates as a result of overgrazing, needle-and-thread, Thurber needlegrass, and Indian ricegrass will decrease while big sagebrush and bottlebrush squirreltail will increase. Annuals will invade. Needlegrasses and Indian ricegrass are the preferred species during all seasons. With further deterioration, bareground will increase and excessive wind erosion in the bare soil interspaces reduces the site productivity.

State and transition model

Custom diagram

Standard 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 text

Ecosystem states

1. Reference State

State 1 submodel, plant communities

1.1. Reference Plant Community

State 1
Reference State

Community 1.1
Reference Plant Community

The potential native plant community is dominated by basin big sagebrush and needle-and-thread. Thurber needlegrass and Indian ricegrass are common. The vegetative composition of the community is approximately 80 percent grasses, 5 percent forbs, and 15 percents shrubs. Approximate ground cover is 50-70 percent (basal and crown).

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	560	720	880
Shrub/Vine	105	135	165
Forb	35	45	55
Total	700	900	1100

Additional community tables

Table 6. Community 1.1 plant community composition

Group	Common name	Symbol	Scientific name	Annual production (lb/acre)	Foliar cover (%)
Grass/Grasslike
1	Perennial, deep-rooted, bunchgrass			505–810
	needle and thread	HECO26	Hesperostipa comata	360–540	–
	Thurber's needlegrass	ACTH7	Achnatherum thurberianum	135–270	–
2	Perennial, deep-rooted, bunchgrass			63–135
	Indian ricegrass	ACHY	Achnatherum hymenoides	45–90	–
	basin wildrye	LECI4	Leymus cinereus	18–45	–
3	Perennial, deep rooted, rhizomatous			9–27
	beardless wildrye	LETR5	Leymus triticoides	9–27	–
5	Other perennial grasses, all			18–54
	squirreltail	ELEL5	Elymus elymoides	0–18	–
	prairie Junegrass	KOMA	Koeleria macrantha	0–18	–
	Sandberg bluegrass	POSE	Poa secunda	0–18	–
	bluebunch wheatgrass	PSSP6	Pseudoroegneria spicata	0–18	–
Forb
7	Perennial, nitrogen-fixing			9–27
	milkvetch	ASTRA	Astragalus	9–27	–
9	Other perennial forbs			9–45
	common yarrow	ACMI2	Achillea millefolium	0–9	–
	hawksbeard	CREPI	Crepis	0–9	–
	buckwheat	ERIOG	Eriogonum	0–9	–
	lupine	LUPIN	Lupinus	0–9	–
	phlox	PHLOX	Phlox	0–9	–
Shrub/Vine
11	Evergreen			90–135
	basin big sagebrush	ARTRT	Artemisia tridentata ssp. tridentata	90–135	–
15	Other shrubs			9–45
	Wyoming big sagebrush	ARTRW8	Artemisia tridentata ssp. wyomingensis	9–45	–
	yellow rabbitbrush	CHVI8	Chrysothamnus viscidiflorus	0–9	–
	antelope bitterbrush	PUTR2	Purshia tridentata	0–9	–

Interpretations

Animal community

Livestock Grazing:

This site is suited to use by cattle, sheep, and horses in the spring, summer, fall, and early winter under a planned grazing system. Use should be postponed until the soils are firm enough to avoid trampling damage and soil compaction.

Native Wildlife Associated with the Potential Climax Community:

Deer
Antelope
Hawks
Songbirds
Rodents

This site will offer food and cover for antelope, mule deer, rodents, and a variety of birds. It is an important wintering area for antelope and mule deer.

Hydrological functions

The soils are in hydrologic group B. The soils of this site have moderately low runoff potential.

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	08/15/2012
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
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):
10-20%
Number of gullies and erosion associated with gullies:
None
Extent of wind scoured, blowouts and/or depositional areas:
None to some, 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):
Slightly resistant to erosion: aggregate stability = 1-2
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
Moderately deep to deep loamy sand to sandy loam (10-20 inches thick): Low OM (1-2%)
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
Moderate to significant ground cover (50-70%) and gentle slopes (0-15%) effectively 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:
Needle and thread grass > Thurber needlegrass > Basin big sagebrush > Indian ricegrass > other grasses > forbs > other shrubs

Sub-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: 900, Normal: 750, Unfavorable: 600 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:
Perennial brush species will increase with deterioration of plant community. Western Juniper readily invades the site. Cheatgrass and Medusahead invade sites that have lost deep rooted perennial grass functional groups.
Perennial plant reproductive capability:
All species should be capable of reproducing anually

Download reference sheet