Natural Resources
Conservation Service
Ecological site R007XY013OR
Sandy Loam 8-10 PZ
Accessed: 11/23/2024
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.
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
R007XY011OR |
Sands 8-10 PZ Sands 8-10" PZ |
---|---|
R007XY012OR |
Sandy 8-10 PZ Sandy 8-10" PZ |
R007XY014OR |
Loamy 8-10 PZ Loamy 8-10" PZ |
Similar sites
R007XY014OR |
Loamy 8-10 PZ Loamy 8-10" PZ (finer surface texture) |
---|---|
R007XY012OR |
Sandy 8-10 PZ Sandy 8-10" PZ (coarser surface texture) |
Table 1. Dominant plant species
Tree |
Not specified |
---|---|
Shrub |
Not specified |
Herbaceous |
Not specified |
Physiographic features
This site occurs on nearly level to gently sloping terraces and terrace fronts. Slopes commonly range from 5-12%, but in extremes range from 0-20%.
Table 2. Representative physiographic features
Landforms |
(1)
Terrace
(2) Alluvial fan |
---|---|
Flooding frequency | None |
Elevation | 122 – 335 m |
Slope | 0 – 20% |
Water table depth | 152 cm |
Aspect | Aspect is not a significant factor |
Climatic features
The annual precipitation ranges from 8 to 10 inches which occurs mostly as rain during the months of November through April. The average annual air temperature is 53 degrees F with extremes ranging from 115 degrees F to -10 degrees F. The frost-free period ranges from 180 to 215 days and the optimum period fro plant growth is from mid-March to mid-June.
Table 3. Representative climatic features
Frost-free period (average) | 215 days |
---|---|
Freeze-free period (average) | 0 days |
Precipitation total (average) | 254 mm |
Figure 2. Monthly average minimum and maximum temperature
Influencing water features
Soil features
The soils of this site are moderately deep to very deep, well drained and formed in wind deposited loess over alluvium or lacustrine sediments. Soil surface textures are fine sandy loam about 5 to 10 inches thick over very fine sandy loam or silt loam subsoils. Gravels may be present in the subsoils. The available water holding capacity ranges fro 4 to 10 inches for the profile. Permeability is moderately rapid to the substratum and moderately rapid in the substratum. Soil reaction is neutral in the surface layer and and mildly to moderately alkaline in the subsoil. Runoff is slow and the erosion hazard is slight for water and moderate for wind.
Table 4. Representative soil features
Surface texture |
(1) Sandy loam (2) Silt loam |
---|---|
Family particle size |
(1) Loamy |
Drainage class | Well drained |
Permeability class | Moderately rapid |
Available water capacity (0-101.6cm) |
10.16 – 25.4 cm |
Ecological dynamics
Any disturbance that reduces plant cover will expose the soils of this site to wind erosion. Uncontrolled wind erosion will result in blow-out depressions and the deposition of coarse fragments will form drifts, hummocks, and dunes downwind. If heavy grazing causes site deterioration, needle and thread and bluebunch wheatgrass will decline. Cheatgrass, mustards, china lettuce, and tarweed will invade the site. Frequent fire may cause an increase in rabbltbrush.
Variability in plant composition on this site results from variations in soil surface textures. Fine textured surfaces favor the establishment of bluebunch wheatgrass. Coarse textured surfaces will encourage a higher proportion of needleandthread.
State and transition model
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
State 1 submodel, plant communities
State 1
HCPC: HECO26-PSSP6-POSE
Community 1.1
HCPC: HECO26-PSSP6-POSE
Needle and thread, bluebunch wheatgrass, sandberg bluegrass community. The HCPC is the interpretative plant community for the site. Variability in palnt composition on this site results from variations in soil subsurface textures. Fine textured surfaces (silts) favor the establishment of bluebunch wheatgrass. Coarse textured surfaces (sands) will encourage a higher proportion of needle and thread.
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 | 342 | 488 | 628 |
Forb | 22 | 39 | 56 |
Shrub/Vine | 11 | 22 | 34 |
Total | 375 | 549 | 718 |
Figure 4. Plant community growth curve (percent production by month). OR2261, B7 SANDS, GOOD CONDITION. RPC growth curve B7 SANDS, 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 | 20 | 25 | 15 | 5 | 5 | 0 | 5 | 10 | 0 | 0 |
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 deep rooted perennial grasses | 224–336 | ||||
needle and thread | HECO26 | Hesperostipa comata | 224–336 | – | ||
2 | Sub-dominant deep rooted perennial grasses | 84–196 | ||||
bluebunch wheatgrass | PSSP6 | Pseudoroegneria spicata | 84–196 | – | ||
3 | Dominant shallow rooted perennial grasses | 28–84 | ||||
Sandberg bluegrass | POSE | Poa secunda | 28–84 | – | ||
5 | Other perennial grasses | 6–11 | ||||
Indian ricegrass | ACHY | Achnatherum hymenoides | 0–6 | – | ||
squirreltail | ELEL5 | Elymus elymoides | 0–6 | – | ||
Forb
|
||||||
7 | Dominant aperennial forbs | 11–34 | ||||
desertparsley | LOMAT | Lomatium | 6–17 | – | ||
phlox | PHLOX | Phlox | 6–17 | – | ||
8 | Sub-dominant perennial forbs | 6–11 | ||||
balsamroot | BALSA | Balsamorhiza | 6–11 | – | ||
9 | Other perennial forbs | 6–11 | ||||
common yarrow | ACMI2 | Achillea millefolium | 0–6 | – | ||
pussytoes | ANTEN | Antennaria | 0–6 | – | ||
milkvetch | ASTRA | Astragalus | 0–6 | – | ||
naked mariposa lily | CANU2 | Calochortus nudus | 0–6 | – | ||
lupine | LUPIN | Lupinus | 0–6 | – | ||
Shrub/Vine
|
||||||
11 | Dominant evergreen shrubs | 6–17 | ||||
basin big sagebrush | ARTRT | Artemisia tridentata ssp. tridentata | 6–17 | – | ||
15 | Other shrubs | 6–17 | ||||
Wyoming big sagebrush | ARTRW8 | Artemisia tridentata ssp. wyomingensis | 0–6 | – | ||
rubber rabbitbrush | ERNA10 | Ericameria nauseosa | 0–6 | – | ||
green rabbitbrush | ERTE18 | Ericameria teretifolia | 0–6 | – | ||
broom snakeweed | GUSA2 | Gutierrezia sarothrae | 0–6 | – |
Interpretations
Animal community
Native Wildlife Associated with the Climax Community:
This site provides nestimg cover for long-billed curlew; and food and cover for mule deer, pronghorn antelope, songbirds, small mammals, and their associated predators.
Wildlife:
The scarcity of water is the limiting factor in the use of this site by wildlife. When located near dependable water sources and irrigated croplands, this site is used extensively by ring-necked pheasants.
Livestock Grazing:
This site is suited to fall, winter, and spring grazing by livestock in a grazing system that provides spring deferment in two of three years.
Hydrological functions
The soils of this site have high intake rates and low runoff potential. The hydrologic soil groups are B and C.
Other information
Caution must be exercised in any vegetative manipulation or excavation work to prevent soil erosion by wind.
Supporting information
Contributors
Alan Bahn
E Ersch (OSU)
J P Repp
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 | 07/25/2012 |
Approved by | Bob Gillaspy |
Approval date | |
Composition (Indicators 10 and 12) based on | Annual Production |
Indicators
-
Number and extent of rills:
None, slight 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):
2-10% -
Number of gullies and erosion associated with gullies:
None -
Extent of wind scoured, blowouts and/or depositional areas:
None to few; 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 to moderately 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 fine sandy loam surface textures; 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%) and gentle (5-12%) slopes should reduce rainfall impact and overland flow; slightly increased flow possible on steeper slopes (up to 20%) -
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 > bluebunch wheatgrass > sandberg bluegrass > dominant forbs > basin big sagebrush >= other shrubs >other grasses >= other forbsSub-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):
In areas with adequate plant cover -
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
Favorable: 800, Normal: 500, 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:
Rabbirbrush, 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 should be capable of reproducing annually
Print Options
Sections
Font
Other
The 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.
Click on box and path labels to scroll to the respective text.