Natural Resources
Conservation Service
Ecological site R034AY146WY
Sands Green River and Great Divide Basins (Sa)
Last updated: 9/28/2023
Accessed: 11/21/2024
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
| R034AY150WY |
Sandy Green River and Great Divide Basins (Sy) Sandy |
|---|
Similar sites
| R034AY246WY |
Sands Foothills and Basins West (Sa) Sands (Sa) 10-14W has higher production. |
|---|---|
| R034AY150WY |
Sandy Green River and Great Divide Basins (Sy) Sandy (Sy) 7-9GR has lower production and shorter shrub height. |
Table 1. Dominant plant species
| Tree |
Not specified |
|---|---|
| Shrub |
Not specified |
| Herbaceous |
Not specified |
Physiographic features
This site usually occurs in an upland position on rolling to very rough topography. Slopes may vary from 5 to 60%, but are generally 10 to 30%.
Table 2. Representative physiographic features
| Landforms |
(1)
Hill
(2) Ridge |
|---|---|
| Flooding frequency | None |
| Ponding frequency | None |
| Elevation | 1,829 – 2,195 m |
| Slope | 5 – 60% |
| Ponding depth | 0 cm |
| Aspect | Aspect is not a significant factor |
Climatic features
Annual precipitation ranges from 7-9 inches per year. Wide fluctuations may occur in yearly precipitation and result in more dry years than those with more than normal precipitation. Temperatures show a wide range between summer and winter and between daily maximums and minimums. This is predominantly due to the high elevation and dry air, which permits rapid incoming and outgoing radiation. Cold air outbreaks in winter move rapidly from northwest to southeast and account for extreme minimum temperatures. Extreme storms may occur during the winter, but most severely affect ranch operations during late winter and spring.
Daytime winds are generally stronger than nighttime and occasional strong storms may bring brief periods of high winds with gusts to more than 50 mph.
Growth of native cool season plants begins about April 15 and continues to about July 15. Some green up of cool season plants may occur in September if moisture is available.
For detailed information visit the Natural Resources Conservation Service National Water and Climate Center at http://www.wcc.nrcs.usda.gov/cgibin/state.pl?state=wy website. Other climate stations representative of this precipitation zone include “Bitter Creek”, ”Farson ”, “Rock Springs FAA AP”, and “Wamsutter” in Sweetwater County; “Church Buttes Gas PLT”, and Mountain View” in Uinta County; “Fontenelle”, “La Barge”, and “Sage 4 NNW” in Lincoln County; and “Big Piney” in Sublette County.
Table 3. Representative climatic features
| Frost-free period (average) | 121 days |
|---|---|
| Freeze-free period (average) | 132 days |
| Precipitation total (average) | 229 mm |
Figure 2. Monthly precipitation range
Figure 3. Monthly average minimum and maximum temperature
Influencing water features
There are no water features associated with this site.
Soil features
The soils of this site formed primarily in aeolian deposits and less commonly in residuum or alluvium. They are deep and moderately deep (more than 15 inches deep) loamy sand and sand soils with neutral pH. This soil can develop into active sand dunes, with the deterioration of cover.
Major Soil Series correlated to this site include: Bodorumpe, Cotopaxi, and Kandaly.
Other Soil Series correlated in MLRA 34 to this site include: Space City, Corlett, and Otterson.
Table 4. Representative soil features
| Surface texture |
(1) Fine sand (2) Loamy fine sand (3) Sand |
|---|---|
| Family particle size |
(1) Sandy |
| Drainage class | Somewhat excessively drained to excessively drained |
| Permeability class | Rapid to very rapid |
| Soil depth | 38 – 152 cm |
| Surface fragment cover <=3" | 0% |
| Surface fragment cover >3" | 0% |
| Available water capacity (0-101.6cm) |
3.81 – 5.33 cm |
| Calcium carbonate equivalent (0-101.6cm) |
0 – 10% |
| Electrical conductivity (0-101.6cm) |
0 – 4 mmhos/cm |
| Sodium adsorption ratio (0-101.6cm) |
0 – 2 |
| Soil reaction (1:1 water) (0-101.6cm) |
7.4 – 9 |
| Subsurface fragment volume <=3" (Depth not specified) |
0% |
| Subsurface fragment volume >3" (Depth not specified) |
0% |
Ecological dynamics
As this site deteriorates from improper grazing management, woody species such as big sagebrush, rabbitbrush, and spiny hopsage will increase. Bunchgrasses such as Indian ricegrass and needleandthread will decrease in frequency and production.
These plant communities narratives may not represent every possibility, but they probably are the most prevalent and repeatable plant communities. The plant composition tables shown above have been developed from the best available knowledge at the time of this revision. As more data is collected, some of these plant communities may be revised or removed, and new ones may be added. None of these plant communities should necessarily be thought of as “Desired Plant Communities”. According to the USDA NRCS National Range and Pasture Handbook, Desired Plant Communities (DPC’s) will be determined by the decision-makers and will meet minimum quality criteria established by the NRCS. The main purpose for including any description of a plant community here is to capture the current knowledge and experience at the time of this revision.
The Reference Plant Community (description follows the plant community diagram) has been determined by study of rangeland relic areas, or areas protected from excessive disturbance. Trends in plant communities going from heavily grazed areas to lightly grazed areas, seasonal use pastures, and historical accounts have also been used.
The following is a State and Transition Model Diagram that illustrates the common plant communities (states) that can occur on the site and the transitions between these communities. The ecological processes will be discussed in more detail in the plant community narratives following the diagram.
State and transition model
More interactive model formats are also available.
View Interactive Models
Click on state and transition labels to scroll to the respective text
State 1 submodel, plant communities
State 2 submodel, plant communities
State 3 submodel, plant communities
State 4 submodel, plant communities
State 1
Needleandthread/Spiny Hopsage (Reference)
Community 1.1
Needleandthread/Spiny Hopsage (Reference)
The interpretive plant community for this site is the Reference Plant Community. This state evolved with grazing by large herbivores and is suited for grazing by domestic livestock. Potential vegetation is estimated at 60% grasses or grass-like plants, 15% forbs, and 25% woody plants. The major grasses include needleandthread, Indian ricegrass, thickspike wheatgrass, and bottlebrush squirreltail. Other grasses include Sandberg bluegrass, prairie junegrass, bluebunch wheatgrass, threeawn, sandhill muhly, galleta, and needleleaf sedge. Silver sagebrush and spiny hopsage are the dominant woody plants. Other woody plants may include big sagebrush, fourwing saltbush, spiny horsebrush, rubber and green rabbitbrush, shadscale, winterfat, and bitterbrush. A typical plant composition for this state consists of needleandthread 15-30%, Indian ricegrass 15-30%, thickspike wheatgrass 10-25%, bottlebrush squirreltail 5-15%, other grasses and grass-like plants 5-15%, perennial forbs 5-15%, silver sagebrush 5-10%, spiny hopsage 5-10%, and 5-15% other woody species. Ground cover, by ocular estimate, varies from 15-25%. The total annual production (air-dry weight) of this state is about 600 pounds per acre, but it can range from about 400 lbs./acre in unfavorable years to about 800 lbs./acre in above average years. This plant community is extremely stable and well adapted to the Cool Central Desertic Basins and Plateaus climatic conditions. The diversity in plant species allows for high drought tolerance. This is a sustainable plant community (site/soil stability, watershed function, and biologic integrity). Transitions or pathways leading to other plant communities are as follows: • Nonuse and No Fire will convert this plant community to the Spiny Hopsage/Bunchgrass State. • Heavy Continuous Season-Long Grazing will convert this plant community to the Spiny Hopsage/Rhizomatous Wheatgrass State. • Wildfire followed by Continuous Season-long Grazing will convert this plant community to the Rabbitbrush/Rhizomatous Wheatgrass State.
Figure 4. 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 | 269 | 404 | 538 |
| Shrub/Vine | 112 | 168 | 224 |
| Forb | 67 | 101 | 135 |
| Total | 448 | 673 | 897 |
Figure 5. Plant community growth curve (percent production by month). WY0401, 7-9GR, UPLAND SITES. ALL UPLAND SITES.
| 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 | 0 | 0 | 10 | 35 | 40 | 10 | 0 | 5 | 0 | 0 | 0 |
State 2
Spiny Hopsage/Bunchgrass
Community 2.1
Spiny Hopsage/Bunchgrass
This plant community is the result of nonuse and the absence of fire. Shrubs dominate the site, lowering herbaceous forage production. Bunchgrasses such as needleandthread and Indian ricegrass dominate the understory. Woody species include big sagebrush, spiny horsebrush, spiny hopsage, rubber and green rabbitbrush, and shadscale. The total annual production (air-dry weight) of this state is about 400 pounds per acre, but it can range from about 250 lbs./acre in unfavorable years to about 600 lbs./acre in above average years. The state is stable and protected from excessive erosion. The biotic integrity of this plant community is usually intact, however forage value will decrease and wildlife values will shift toward different species. The watershed is functioning. Transitional pathways leading to other plant communities are as follows: • Brush Management followed by deferment for 1 to 2 years as part of a Prescribed Grazing plan will return this state to near Reference Plant Community (Needleandthread/Spiny Hopsage State). Care should be taken when planning brush management to consider wildlife habitat and critical winter ranges.
Figure 6. Plant community growth curve (percent production by month). WY0401, 7-9GR, UPLAND SITES. ALL UPLAND SITES.
| 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 | 0 | 0 | 10 | 35 | 40 | 10 | 0 | 5 | 0 | 0 | 0 |
State 3
Spiny Hopsage/Rhizomatous Wheatgrass
Community 3.1
Spiny Hopsage/Rhizomatous Wheatgrass
This plant community is the result of continuous season-long grazing. It is dominated by shrubs, bare ground, thickspike wheatgrass, and both annual and perennial forbs. Common forbs include scurfpea and sagebrush gilia. The total annual production (air-dry weight) of this state is about 200 pounds per acre, but it can range from about 100 lbs./acre in unfavorable years to about 400 lbs./acre in above average years. Soil erosion is accelerated because of increased bare ground. The biotic community has been compromised, but is relatively stable. The watershed is functioning, but is at risk of further degradation. Water flow patterns and pedestals are obvious. Infiltration is reduced and runoff is increased. Transitional pathways leading to other plant communities are as follows: • Brush Management followed by deferment for 1 to 2 years as part of a Prescribed Grazing plan will return this state to near Reference Plant Community (Needleandthread/Spiny Hopsage State). Care should be taken when planning brush management to consider wildlife habitat and critical winter ranges. • Wildfire OR Brush Management followed by Continuous Season-long Grazing will convert this plant community to the Rabbitbrush/Rhizomatous Wheatgrass State.
Figure 7. Plant community growth curve (percent production by month). WY0401, 7-9GR, UPLAND SITES. ALL UPLAND SITES.
| 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 | 0 | 0 | 10 | 35 | 40 | 10 | 0 | 5 | 0 | 0 | 0 |
State 4
Rabbitbrush/Rhizomatous Wheatgrass
Community 4.1
Rabbitbrush/Rhizomatous Wheatgrass
This plant community is the result of severe disturbance such as brush management or wildfire followed by improper grazing. It is dominated by sprouting shrubs such as rabbitbrush. Rhizomatous grasses such as thickspike wheatgrass, and unpalatable annual and perennial forbs are in the understory. There is a substantial amount of bare ground. The total annual production (air-dry weight) of this state is about 150 pounds per acre, but it can range from about 50 lbs./acre in unfavorable years to about 350 lbs./acre in above average years. The soil is not protected and erosion will increase if management is not changed. The biotic integrity may be reduced due to low vegetative production and blowing sand. The watershed is functioning at risk. Transitional pathways leading to other plant communities are as follows: • Brush Management followed by deferment for 1 to 2 years as part of a Prescribed Grazing plan will return this plant community to near Reference Plant Community (Needleandthread/Spiny Hopsage State). Care should be taken when planning brush management to consider wildlife habitat and critical winter ranges.
Figure 8. Plant community growth curve (percent production by month). WY0401, 7-9GR, UPLAND SITES. ALL UPLAND SITES.
| 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 | 0 | 0 | 10 | 35 | 40 | 10 | 0 | 5 | 0 | 0 | 0 |
Transition T1-2
State 1 to 2
Nonuse and No Fire will convert this plant community to the Spiny Hopsage/Bunchgrass State.
Transition T1-3
State 1 to 3
Heavy Continuous Season-Long Grazing will convert this plant community to the Spiny Hopsage/Rhizomatous Wheatgrass State.
Transition T1-4
State 1 to 4
Wildfire followed by Continuous Season-long Grazing will convert this plant community to the Rabbitbrush/Rhizomatous Wheatgrass State.
Restoration pathway R2-1
State 2 to 1
Brush Management followed by deferment for 1 to 2 years as part of a Prescribed Grazing plan will return this state to near Reference Plant Community (Needleandthread/Spiny Hopsage State). Care should be taken when planning brush management to consider wildlife habitat and critical winter ranges.
Restoration pathway R3-1
State 3 to 1
Brush Management followed by deferment for 1 to 2 years as part of a Prescribed Grazing plan will return this state to near Reference Plant Community (Needleandthread/Spiny Hopsage State). Care should be taken when planning brush management to consider wildlife habitat and critical winter ranges.
Transition T3-4
State 3 to 4
Wildfire OR Brush Management followed by Continuous Season-long Grazing will convert this plant community to the Rabbitbrush/Rhizomatous Wheatgrass State.
Restoration pathway R4-1
State 4 to 1
Brush Management followed by deferment for 1 to 2 years as part of a Prescribed Grazing plan will return this plant community to near Reference Plant Community (Needleandthread/Spiny Hopsage State). Care should be taken when planning brush management to consider wildlife habitat and critical winter ranges.
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 | 101–202 | |||||
| needle and thread | HECO26 | Hesperostipa comata | 101–90 | – | ||
| 2 | 101–202 | |||||
| Indian ricegrass | ACHY | Achnatherum hymenoides | 101–202 | – | ||
| 3 | 67–168 | |||||
| thickspike wheatgrass | ELLAL | Elymus lanceolatus ssp. lanceolatus | 67–168 | – | ||
| 4 | 34–101 | |||||
| squirreltail | ELEL5 | Elymus elymoides | 34–101 | – | ||
| 5 | 34–101 | |||||
| Grass, perennial | 2GP | Grass, perennial | 0–34 | – | ||
| threeawn | ARIST | Aristida | 0–34 | – | ||
| needleleaf sedge | CADU6 | Carex duriuscula | 0–34 | – | ||
| prairie Junegrass | KOMA | Koeleria macrantha | 0–34 | – | ||
| sandhill muhly | MUPU2 | Muhlenbergia pungens | 0–34 | – | ||
| galleta grass | PLEUR12 | Pleuraphis | 0–34 | – | ||
| Sandberg bluegrass | POSE | Poa secunda | 0–34 | – | ||
| bluebunch wheatgrass | PSSP6 | Pseudoroegneria spicata | 0–34 | – | ||
| sand dropseed | SPCR | Sporobolus cryptandrus | 0–34 | – | ||
|
Forb
|
||||||
| 6 | 34–101 | |||||
| Forb, perennial | 2FP | Forb, perennial | 0–34 | – | ||
| common yarrow | ACMI2 | Achillea millefolium | 0–34 | – | ||
| rosy pussytoes | ANRO2 | Antennaria rosea | 0–34 | – | ||
| sandwort | ARENA | Arenaria | 0–34 | – | ||
| milkvetch | ASTRA | Astragalus | 0–34 | – | ||
| Indian paintbrush | CASTI2 | Castilleja | 0–34 | – | ||
| fleabane | ERIGE2 | Erigeron | 0–34 | – | ||
| buckwheat | ERIOG | Eriogonum | 0–34 | – | ||
| aster | EUCEP2 | Eucephalus | 0–34 | – | ||
| toadflax | LINAR | Linaria | 0–34 | – | ||
| granite prickly phlox | LIPU11 | Linanthus pungens | 0–34 | – | ||
| desertparsley | LOMAT | Lomatium | 0–34 | – | ||
| beardtongue | PENST | Penstemon | 0–34 | – | ||
| phacelia | PHACE | Phacelia | 0–34 | – | ||
| spiny phlox | PHHO | Phlox hoodii | 0–34 | – | ||
| slimflower scurfpea | PSTE5 | Psoralidium tenuiflorum | 0–34 | – | ||
| scarlet globemallow | SPCO | Sphaeralcea coccinea | 0–34 | – | ||
| clover | TRIFO | Trifolium | 0–34 | – | ||
|
Shrub/Vine
|
||||||
| 7 | 34–67 | |||||
| silver sagebrush | ARCAC5 | Artemisia cana ssp. cana | 34–67 | – | ||
| 8 | 34–67 | |||||
| spiny hopsage | GRSP | Grayia spinosa | 34–67 | – | ||
| 9 | 34–101 | |||||
| prairie sagewort | ARFR4 | Artemisia frigida | 0–34 | – | ||
| big sagebrush | ARTR2 | Artemisia tridentata | 0–34 | – | ||
| fourwing saltbush | ATCA2 | Atriplex canescens | 0–34 | – | ||
| shadscale saltbush | ATCO | Atriplex confertifolia | 0–34 | – | ||
| yellow rabbitbrush | CHVI8 | Chrysothamnus viscidiflorus | 0–34 | – | ||
| rubber rabbitbrush | ERNA10 | Ericameria nauseosa | 0–34 | – | ||
| winterfat | KRLA2 | Krascheninnikovia lanata | 0–34 | – | ||
| antelope bitterbrush | PUTR2 | Purshia tridentata | 0–34 | – | ||
| horsebrush | TETRA3 | Tetradymia | 0–34 | – | ||
Interpretations
Animal community
Animal Community – Wildlife Interpretations
Needleandthread/Spiny Hopsage Plant Community (HCPC): Suitable thermal and escape cover for mule deer may be limited due to the low height of woody plants. However, topographical variations could provide some escape cover. Sagebrush, which can approach 15% protein and 40-60% digestibility, provides important winter forage for mule deer and antelope. Year-round habitat is provided for sage grouse and many other sagebrush obligate species such as the sage sparrow, Brewer’s sparrow, sage thrasher, pygmy rabbit, sagebrush vole, horned lizard, and pronghorn antelope. Other birds that would frequent this plant community include horned larks and golden eagles.
Spiny Hopsage/Bunchgrass Plant Community: This plant community may be useful for the same wildlife that would use the Historic Climax Plant Community.
Spiny Hopsage/Rhizomatous Wheatgrass Plant Community: These communities are unstable due to moving sand dunes. They provide a unique temporary habitat for some small mammals and birds.
Rabbitbrush/Rhizomatous Wheatgrass Plant Community: These communities are unstable due to moving sand dunes. They provide a unique temporary habitat for some small mammals and birds.
Animal Community – Grazing Interpretations
The following table lists suggested stocking rates for cattle under continuous season-long grazing under normal growing conditions. These are conservative estimates that should be used only as guidelines in the initial stages of the conservation planning process. Often, the current plant composition does not entirely match any particular plant community (as described in this ecological site description). Because of this, a field visit is recommended, in all cases, to document plant composition and production. More precise carrying capacity estimates should eventually be calculated using this information along with animal preference data, particularly when grazers other than cattle are involved. Under more intensive grazing management, improved harvest efficiencies can result in an increased carrying capacity.
Plant Community Production (lb./ac) and Carrying Capacity* (AUM/ac)
Needleandthread/Spiny Hopsage (HCPC)400-800 lb./ac and .18 AUM/ac
Spiny Hopsage/Bunchgrass 250-600 lb./ac and .12 AUM/ac
Spiny Hopsage/Rhizomatous Wheatgrass 100-400 lb./ac and .07 AUM/ac
Rabbitbrush/ Rhizomatous Wheatgrass 50-350 lb./ac and .05 AUM/ac
* - Continuous, season-long grazing by cattle under average growing conditions.
Grazing by domestic livestock is one of the major income-producing industries in the area. Rangeland in this area may provide yearlong forage for cattle, sheep, or horses. During the dormant period, the forage for livestock use needs to be supplemented with protein because the quality does not meet minimum livestock requirements.
Hydrological functions
Water is the principal factor limiting forage production on this site. This site is dominated by soils in hydrologic group A, with localized areas in hydrologic group B. Infiltration potential for this site varies from moderately rapid to very rapid depending on soil hydrologic group and ground cover. Runoff varies from very low to moderately low (refer to Part 630, NRCS National Engineering Handbook for detailed hydrology information).
Rills and gullies should not typically be present. Water flow patterns should be barely distinguishable if at all present. Litter typically falls in place, and signs of movement are not common. Chemical and physical crusts are rare to non-existent.
Recreational uses
This site provides hunting opportunities for upland game species. The wide variety of plants which bloom from spring until fall have an esthetic value that appeals to visitors. The sandy nature of the soils appeals to Off-Road Vehicle (ORV) users.
Wood products
No appreciable wood products are present on the site.
Other products
None noted.
Supporting information
Inventory data references
Information presented here has been derived from NRCS clipping data and other inventory data. Field observations from range trained personnel were also used. Those involved in developing this site include: Bill Christensen, Range Management Specialist, NRCS; Karen Clause, Range Management Specialist, NRCS; and Everet Bainter, Range Management Specialist, NRCS. Other sources used as references include: USDA NRCS Water and Climate Center, USDA NRCS National Range and Pasture Handbook, and USDA NRCS Soil Surveys from various counties.
Contributors
Karen Clause
Approval
Kirt Walstad, 9/28/2023
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) | K. Clause, B. Brazee, E. Bainter |
|---|---|
| Contact for lead author | karen.clause@wy.usda.gov or 307-367-2257 |
| Date | 03/16/2007 |
| Approved by | Kirt Walstad |
| Approval date | |
| Composition (Indicators 10 and 12) based on | Annual Production |
Indicators
-
Number and extent of rills:
Rare to nonexistent. -
Presence of water flow patterns:
Barely observable. -
Number and height of erosional pedestals or terracettes:
Rare to nonexistent. -
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
Bare ground can range from 30-60%. -
Number of gullies and erosion associated with gullies:
Active gullies should not be present. -
Extent of wind scoured, blowouts and/or depositional areas:
Wind scouring and deposition evident and associated with dune topography typical of this site. -
Amount of litter movement (describe size and distance expected to travel):
Herbaceous litter expected to move due to wind. Large woody debris from sagebrush will show no movement. -
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
Soil Stability Index ratings range from 1 (interspaces) to 5 (under plant canopy), but average values should be 2.5 or greater. -
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
Typically an A-horizon of 2-8 inches (5-20 cm) with single grain structure that is brown to light brownish gray (hues 10YR or 2.5Y, values 5-7, chromas 2-3) in color with OM of less than .5%. -
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
Plant community consists of 50-70% grasses, 15% forbs, and 15-35% shrubs. Evenly distributed plant canopy (30-50%) and litter plus rapid infiltration rates result in minimal runoff. Basal cover typically is less than 5% for this site and does very little to effect runoff on this site. -
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:
Sub-dominant:
Other:
Additional:
Mid-size, cool season bunchgrasses> perennial shrubs>cool season rhizomatous grasses>perennial forbs -
Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
Minimal decadence, typically associated with shrub component. -
Average percent litter cover (%) and depth ( in):
Litter ranges from 5-20% of total canopy measurement with total litter (including beneath the plant canopy) from 10-40% expected. Herbaceous litter depth is typically very shallow, ranging from 1-5mm. Woody litter can be up to a couple inches (4-6 cm). -
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
English: 400-800 lb/ac (600 lb/ac average); Metric 448-896 kg/ha (672 kg/ha average). -
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:
Bare ground greater than 60% is the most common indicator of a threshold being crossed. Rabbitbrush, basin big sagebrush, Sandberg bluegrass, and phlox are common increasers. Annual weeds such as halogeton, kochia, and Russian thistle are common invasive species in disturbed sites. -
Perennial plant reproductive capability:
All species are capable of reproducing, except in drought years.
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