Natural Resources
Conservation Service
Ecological site GX064X01X015
Loamy 14-17" PZ
Last updated: 12/16/2024
Accessed: 12/30/2024
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.
MLRA notes
Major Land Resource Area (MLRA): 064X–Mixed Sandy and Silty Tableland and Badlands
The Mixed Sandy and Silty Tableland and Badlands (MLRA 64) is shared almost equally between South Dakota (42 percent) and Nebraska (41 percent). A small portion is in Wyoming (17 percent). The MLRA consists of 11,895 square miles. The towns of Kadoka and Pine Ridge, South Dakota; Chadron and Alliance, Nebraska; and Lusk, Wyoming, are all within the boundaries of this MLRA.
The following areas of special interest are in this MLRA: Agate Fossil Beds National Monument, Chadron State Park, Fort Robinson State Park, and the Pine Ridge Indian Reservation; parts of the Oglala and Buffalo Gap National Grasslands, which are in the Nebraska National Forest; and nearly all of Badlands National Park. The Badlands are internationally renowned for their Oligocene vertebrate fossils.
The northern section of the MLRA consists of old plateaus and terraces that have been deeply eroded by wind, water, and time. The southern section consists of nearly level to broad intervalley remnants of smooth fluvial plains. These two sections are separated by the Pine Ridge escarpment. Elevations gradually increase from 2,950 to 5,073 feet from east to west. The main drainageway through Badlands National Park is the White River. The headwaters of both the White and Niobrara Rivers are in MLRA 64. The Pine Ridge escarpment is at the northernmost extent of the Ogallala Aquifer.
Tertiary continental sediments consisting of sandstone, siltstone, and claystone underlie most of the area. Many of the bedrock units in the southern third of the MLRA are covered by loess. Soils range from shallow to very deep and from generally well drained to excessively drained. They are loamy or sandy. The Badlands consist of stream-laid layers of silt, clay, and sand mixed with layers of volcanic ash.
Average annual precipitation for the area is 14 to 20 inches. Most of the rainfall occurs as frontal storms in the spring and early summer. This area supports a mixture of short-, mid-, and tall-statured warm- and cool-season grasses. On the Pine Ridge Escarpment, these plants grow in association with ponderosa pine, Rocky Mountain juniper, western snowberry, skunkbush sumac, common chokecherry, and rose. Wyoming big sagebrush grows in minor amounts in the drier, far western portion of the MLRA; however, small remnant stands can be found in the eastern portion of the Oglala National Grassland in Nebraska.
Sixty percent of the MLRA is grassland, 11 percent of which is under Federal management. Twenty-two percent of the area is used as cropland, and 4 percent is forested. Major resource concerns include wind erosion, water erosion, and surface water quality (USDA-NRCS, 2006, Ag Handbook 296).
For development of ecological sites, MLRA 64 is divided into two precipitation zones (PZ): 14 to 17 inches per year and 17 to 20 inches per year. The wetter zone extends from the western end of the Pine Ridge Escarpment near Lusk, Wyoming, eastward along the escarpment through Nebraska and into the Big Badlands area of South Dakota. The drier zone extends from Wyoming eastward to Alliance and Oshkosh, Nebraska, south of the Pine Ridge Escarpment. MLRA 64 stops at the western edge of the Nebraska Sand Hills (MLRA 65).
A unique geologic area known as the Hartville Uplift is in the far southwest corner of the 14 to 17 inch precipitation zone. The Hartville Uplift is an elongated, north-northwest-oriented, broad domal arch of Laramide age (70-50 million years ago). It extends approximately 45 miles between Guernsey and Lusk, Wyoming, and is 15 miles wide at its widest point. Erosion has exposed a core of granite and Precambrian metasedimentary and metavolcanic rocks (Steele et al., 2018). In addition to the ecological sites in the 14 to 17 inch precipitation zone of MLRA 64, three unique ecological site descriptions were developed to describe the soils and plant community dynamics in the Hartville Uplift.
Classification relationships
USDA Land Resource Region G—Western Great Plains Range and Irrigated Region:
Major Land Resource Area (MLRA) 64—Mixed Sandy and Silty Tableland and Badlands
U.S. Environmental Protection Agency (EPA)
Level IV Ecoregions of the Conterminous United States:
High Plains—25:
Pine Ridge Escarpment—25a.
Flat to Rolling Plains—25d.
Pine Bluffs and Hills—25f.
Sandy and Silty Tablelands—25g.
Northwestern Great Plains—43:
White River Badlands—43h.
Keya Paha Tablelands—43i.
USDA Forest Service
Ecological Subregions: Sections and Subsections of Conterminous United States:
Great Plains and Palouse Dry Steppe Province—331:
Western Great Plains Section—331F:
Subsections:
Shale Scablands—331Fb.
White River Badlands—331Fh.
Pine Ridge Escarpment—331Fj.
High Plains—331Fk.
Hartville Uplift—331Fm.
Western Nebraska Sandy and Silty Tablelands—331Fn.
Keye Paha Tablelands—331Ft.
Ecological site concept
The Loamy 14-17" PZ ecological site occurs throughout the drier portion of MLRA 64. It is located on upland landscapes and does not receive additional moisture from runoff or overflow. The typical slopes range is from 0 to 30 percent. Soils are deep, (greater than 20 inches) with surface textures range from very fine sandy loam to loam. Subsurface textures range from loam to clay loam. The vegetation in the Reference State consists of a mix of cool- and warm-season grasses, however, mid-statured cool-season grasses will be the dominant group. Rhizomatous wheatgrass, needle and thread, and green needlegrass are the dominant cool-season grasses, while blue grama and buffalograss are the dominant warm-season grasses. Forbs are common and diverse. Dominant shrubs include rose, winterfat, cactus, and occasionally Wyoming big sagebrush in the far western portion of the MLRA. The Loamy 14-17” PZ site is susceptible to invasion of non- native, cool-season grasses, especially field brome and cheatgrass.
Associated sites
| R064XY037NE |
Thin Upland The Thin Upland site will be found on steeper slopes, typically on higher landscape positions than the Loamy 14-17” PZ site. |
|---|---|
| R064XY011NE |
Sandy 14-17" PZ The Sandy 14-17” PZ site can be found adjacent to the Loam 14-17” PZ sites. |
| R064XY026NE |
Loamy Overflow The Loamy Overflow sites can be found on lower landscape position adjacent to the Loamy 14-17” PZ sites. |
Similar sites
| R064XY014NE |
Clayey 14-17" PZ The Clayey 14-17” PZ site will have more green needlegrass and less needle and thread than the Loamy 14-17” PZ site. |
|---|---|
| R064XY026NE |
Loamy Overflow The Loamy Overflow site will have more big bluestem, less needle and thread, and higher forage production than the Loamy 14-17” PZ site. |
Table 1. Dominant plant species
| Tree |
Not specified |
|---|---|
| Shrub |
Not specified |
| Herbaceous |
(1) Pascopyrum smithii |
Legacy ID
R064XY015NE
Physiographic features
This Loamy 14-17” PZ ecological site occurs on gently undulating to rolling plains and low hills.
Table 2. Representative physiographic features
| Landforms |
(1)
Alluvial fan
(2) Alluvial flat (3) Hill |
|---|---|
| Flooding frequency | None |
| Ponding frequency | None |
| Elevation | 2,900 – 4,000 ft |
| Slope | 30% |
| Aspect | Aspect is not a significant factor |
Climatic features
MLRA 64 has a continental climate consisting of cold winters and hot summers, low humidity, light rainfall, and ample sunshine. Extremes in temperature are common in some years. The climate results from MLRA 64 being near the geographic center of North America. There are few natural barriers on the Northern Great Plains. Air masses move freely across the plains and account for rapid changes in temperature.
Average annual precipitation ranges from 14 to 17 inches per year. The normal average annual temperature is about 46 °F. January is the coldest month with average temperatures ranging from about 24 °F (Lusk 2 SW, WY) to about 26 °F (Hemingford, NE). July is the warmest month with average temperatures ranging from about 69 °F (Lusk 2 SW, WY) to about 73 °F (Hemingford, NE). The range of normal average monthly temperatures between the coldest and warmest months is about 50 °F. This large annual range attests to the continental nature of the climate of this area. Wind speeds are estimated to average about 11 miles per hour annually, ranging from about 13 miles per hour during the spring to about 10 miles per hour during the summer. Daytime winds are generally stronger than nighttime winds. Occasionally, strong storms bring brief periods of high winds with gusts to more than 50 miles per hour.
Growth of cool-season plants begins in early to mid-March, slowing or ceasing in late June. Warm-season plants begin growth about mid-May and continue to early or mid-September. Cool-season plants may green-up in September and October if adequate soil moisture is present.
Table 3. Representative climatic features
| Frost-free period (characteristic range) | 85-121 days |
|---|---|
| Freeze-free period (characteristic range) | 106-131 days |
| Precipitation total (characteristic range) | 15-16 in |
| Frost-free period (actual range) | 62-123 days |
| Freeze-free period (actual range) | 93-139 days |
| Precipitation total (actual range) | 15-17 in |
| Frost-free period (average) | 98 days |
| Freeze-free period (average) | 120 days |
| Precipitation total (average) | 16 in |
Figure 2. Monthly precipitation range
Figure 3. Monthly minimum temperature range
Figure 4. Monthly maximum temperature range
Figure 5. Monthly average minimum and maximum temperature
Figure 6. Annual precipitation pattern
Figure 7. Annual average temperature pattern
Climate stations used
-
(1) AGATE 3 E [USC00250030], Harrison, NE
-
(2) HEMINGFORD [USC00253755], Hemingford, NE
-
(3) HAY SPRINGS 12 S [USC00253715], Hay Springs, NE
-
(4) LUSK 2 SW [USC00485830], Lusk, WY
-
(5) TORRINGTON 29N [USC00488997], Jay Em, WY
-
(6) ALLIANCE 1WNW [USC00250130], Alliance, NE
Influencing water features
No significant water features influence this site.
Wetland description
Not Applicable.
Soil features
The features common to soils in the Loamy 14-17” PZ ecological site are the very fine sandy loam- to loam-textured surface soils and slopes of 0 to 30 percent. The soils in this site are well to somewhat excessively drained and formed in soft siltstone, sandstone, or alluvium. The surface layer is 5 to 25 inches thick. The texture of the profile ranges from loamy very fine sand to clay loam. The soils have a moderate infiltration rate. This site should show slight to no evidence of rills, wind-scoured areas, or pedestalled plants. Water flow paths are broken, irregular in appearance or discontinuous with numerous debris dams or vegetative barriers. The soil surface is stable and intact. Subsurface soil layers are not restrictive to water movement and root penetration.
Major soils correlated to the Loamy 14-17” PZ ecological site include: Alliance, Creighton, Duroc, Hemingford, Kadoka, Keith, Oglala, Rosebud, Satanta, and Thirtynine.
These soils are susceptible to wind and water erosion. The hazard of water erosion increases on slopes greater than about 15 percent. Loss of 50 percent or more of the surface layer of the soils on this site can result in a shift in species composition and/or production.
More information regarding the soil is available in soil survey reports. Contact the local USDA Service Center for details specific to your area of interest, or go online to access USDA’s Web Soil Survey.
Table 4. Representative soil features
| Parent material |
(1)
Alluvium
–
sandstone and siltstone
|
|---|---|
| Surface texture |
(1) Very fine sandy loam (2) Loam |
| Family particle size |
(1) Loamy |
| Drainage class | Well drained to somewhat excessively drained |
| Permeability class | Moderately slow to moderate |
| Soil depth | 20 – 80 in |
| Available water capacity (0-40in) |
5 – 9 in |
| Calcium carbonate equivalent (0-40in) |
15% |
| Electrical conductivity (0-40in) |
2 mmhos/cm |
| Sodium adsorption ratio (0-40in) |
5 |
| Soil reaction (1:1 water) (0-40in) |
6.1 – 9 |
| Subsurface fragment volume <=3" (Depth not specified) |
30% |
| Subsurface fragment volume >3" (Depth not specified) |
15% |
Ecological dynamics
The Loamy 14-17” PZ ecological site developed under Northern Great Plains climatic conditions; light to severe grazing by bison and other large herbivores; sporadic, natural or human-caused wildfire (often of light intensities); and other biotic and abiotic factors that typically influence soil and site development. Changes occur in the plant communities due to short-term weather variations, effects of native and exotic plant and animal species, and management actions. Although the following plant community descriptions are typical of the transitions between communities, severe disturbances, such as periods of well below average precipitation and the introduction of non-native cool-season grasses, can cause significant shifts in plant communities and species composition.
Continuous season-long grazing (during the typical growing season of May through October) and/or repeated seasonal grazing (e.g., every spring, every summer) without adequate recovery periods following each grazing occurrence causes this site to depart from the Rhizomatous Wheatgrass-Needle and Thread-Blue Grama Plant Community (1.1). Blue grama will increase and eventually develop into a sod.
Rhizomatous wheatgrass will increase initially and then begin to decrease. Needle and thread, green needlegrass, and sideoats grama will decrease in frequency and production. Frequent and severe defoliation or heavy disturbance will cause threeawns and annuals to increase and dominate the site. Extended periods of non-use, lack of fire, or continuous seasonal grazing will result in a plant community dominated by cool-season grasses and excessive litter and annuals.
Historically, mechanical treatment was an option to improve forage production and plant species composition on rangeland on this site. Mechanical treatments included contour furrowing, contour pitting, terracing, chiseling, and disking. These treatments were used to break up a sod-bound vegetative condition or compacted soils, resulting in less runoff and better infiltration. Many of these treatments were implemented from the 1930s through the 1970s but have shown to have no real long-term benefits for improving production. The lack of benefit is primarily due to improper grazing management following the renovation practice. Another drawback, in addition to the cost, is the practices result in a permanently rough ground surface.
Interpretations are primarily based on the Rhizomatous Wheatgrass-Needle and Thread-Blue Grama Plant Community (1.1). It has been determined by study of rangeland relic areas, areas protected from excessive disturbance, and areas under long-term rotational grazing regimes. Trends in plant community dynamics ranging from heavily grazed to lightly grazed areas, seasonal use pastures, and historical accounts also have been used. Plant communities, states, transitional pathways, and thresholds have been determined through similar studies and experience.
The following state-and-transition diagram illustrates the common plant communities on the site and the transition pathways between communities. The ecological processes are discussed in more detail in the plant community descriptions following the diagram.
State and transition model
Figure 8. Loamy 14-17" PZ - R064XY015NE.
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Ecosystem states
States 1, 6, 2 and 5 (additional transitions)
States 2 and 6 (additional transitions)
State 1 submodel, plant communities
State 2 submodel, plant communities
State 3 submodel, plant communities
State 5 submodel, plant communities
State 6 submodel, plant communities
State 1
Reference State
The Reference State represents the best estimate of the natural range of variability that dominated the dynamics in this ecological site prior to European settlement. This site in the Reference State (1.0) is dominated by cool-season grasses and subdominant warm-season grass. Grazing or the lack of grazing, fire, and drought are the major drivers between plant communities. Continuous season-long grazing can push this State to a warm-season shortgrass-dominated State (2.0). Non-use, no fire, and invasion of non-native cool-season grasses will result in a transition to a Native/Invaded State (4.0).
Community 1.1
Rhizomatous Wheatgrass-Needle and Thread-Blue Grama
Interpretations are based primarily on the Western Wheatgrass-Needle and Thread-Blue Grama Plant Community. This is also considered to be the Reference Plant Community (1.1). The plant community can be found on areas that are properly managed with grazing and/or prescribed burning, and sometimes on areas receiving occasional short periods of rest. The potential vegetation is about 75 percent grasses, 10 percent grass-like plants, 10 percent forbs, and 5 percent shrubs. The dominant grasses include western wheatgrass, thickspike wheatgrass, needle and thread, and blue grama. Other grasses and grass-likes may include buffalograss, green needlegrass, and threadleaf sedge. The dominant forbs include, Cuman ragweed, cudweed sagewort, and prairie coneflower. Dominant shrubs in this community include rose, winterfat, cactus, fringed sagewort, and occasionally snowberry. In the far western portion of the MLRA, Wyoming big sagebrush may be present is small amounts. This plant community is well adapted to the Northern Great Plains climatic conditions. Individual species can vary greatly in production depending on growing conditions (timing and amount of precipitation and temperature). Plant litter is properly distributed with some movement off-site and natural plant mortality is low. The diversity in plant species allows for high drought tolerance. This is a sustainable plant community in terms of soil stability and watershed function. Moderate or high available water capacity provides a favorable soil-water- plant relationship.
Figure 9. 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 | 915 | 1575 | 2130 |
| Forb | 85 | 135 | 185 |
| Shrub/Vine | 0 | 90 | 185 |
| Total | 1000 | 1800 | 2500 |
Figure 10. Plant community growth curve (percent production by month). NE6401, Pine Ridge/Badlands, cool-season dominant. Cool-season dominant.
| Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec |
|---|---|---|---|---|---|---|---|---|---|---|---|
| J | F | M | A | M | J | J | A | S | O | N | D |
| 5 | 15 | 28 | 30 | 10 | 2 | 5 | 5 |
Community 1.2
Blue Grama-Rhizomatous Wheatgrass/Threadleaf Sedge
This plant community develops with early continuous seasonal grazing and late winter grazing (i.e., grazing at the onset of the growth curve every year). This plant community can also develop from continuous season-long grazing and heavy grazing in combination with drought. The potential vegetation is made up of approximately 75 percent grasses, 10 percent grass-likes, 10 percent forbs, and 5 percent shrubs. The dominant grasses include blue grama and rhizomatous wheatgrass. Other grasses or grass-like species are threadleaf sedge, buffalograss, and needle and thread. Forbs include scarlet globemallow, scurfpea, Cuman ragweed, and perennial aster species. Shrubs include rose, broom snakeweed, fringed sagewort, and pricklypear cactus. Compared to the Rhizomatous Wheatgrass-Needle and Thread-Blue Grama Plant Community (1.1), blue grama and threadleaf sedge have increased. Rhizomatous wheatgrass and needle and thread have decreased in composition. Annual bromes and annual forbs can invade the site. Plant diversity is moderate. Shortgrasses dominate the structure of the community. The plant community tends to be resilient if disturbance is not long term. Species such as blue grama and threadleaf sedge are very adapted to grazing; however, western wheatgrass, needle and thread, and the more palatable forbs will decrease in the community with recurrent disturbance and/or climatic fluctuations. Soil erosion is low. Compared to the Rhizomatous Wheatgrass-Needle and Thread-Blue Grama Plant Community, water infiltration is slightly lower, and runoff is somewhat higher. Typically, the runoff is very clean because of the low potential for soil erosion.
Figure 11. Annual production by plant type (representative values) or group (midpoint values)
Table 6. Annual production by plant type
| Plant type | Low (lb/acre) |
Representative value (lb/acre) |
High (lb/acre) |
|---|---|---|---|
| Grass/Grasslike | 745 | 1020 | 1290 |
| Forb | 55 | 120 | 185 |
| Shrub/Vine | 0 | 60 | 125 |
| Total | 800 | 1200 | 1600 |
Figure 12. Plant community growth curve (percent production by month). NE6403, Pine Ridge/Badlands, cool-season/warm-season co-dominant. Cool-season, warm-season co-dominant.
| Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec |
|---|---|---|---|---|---|---|---|---|---|---|---|
| J | F | M | A | M | J | J | A | S | O | N | D |
| 5 | 10 | 20 | 25 | 20 | 10 | 5 | 5 |
Pathway 1.1A
Community 1.1 to 1.2
Continuous seasonal grazing during the active growing period of cool-season plants, or late-season winter grazing, or continuous season-long grazing, or heavy grazing in combination with drought will lead to the Blue Grama-Rhizomatous Wheatgrass/Threadleaf Sedge Plant Community (1.2).
Pathway 1.2A
Community 1.2 to 1.1
Prescribed grazing that allows for adequate plant recovery periods and a return to normal precipitation patterns will move this plant community to the Rhizomatous Wheatgrass-Needle and Thread-Blue Grama Plant Community (1.1). Periods of non-use or deferment may be a management option to reach the Rhizomatous Wheatgrass-Needle and Thread-Blue Grama Plant Community.
Conservation practices
| Prescribed Grazing |
|---|
State 2
Shortgrass Sod State
The Shortgrass Sod State is dominated by shortgrass species and upland sedges. This State is the result of grazing patterns that did not provide adequate recovery time for cool-season wheat grasses and needlegrasses. If heavy disturbance such as frequent and severe defoliation and livestock concentration continues, pioneer perennials and annual grass and forb species may become dominant. The hydrologic function is dramatically altered in the Shortgrass Sod State. Runoff is high, and infiltration is low. This State is very resistant to change through grazing management alone.
Community 2.1
Blue Grama/Threadleaf Sedge
This plant community develops with continuous season-long grazing, continuous seasonal grazing or heavy grazing in combination with drought. It is a dense sod, made up of primarily warm-season shortgrasses and grass-like sedges. The cool-season mid-grasses have been significantly reduced. The dominant grass is blue grama. Other grasses include buffalograss, and threeawn. Palatable forbs initiate avoidance mechanisms and are difficult to find on the site. Species such as scarlet globemallow, Cuman ragweed, and cudweed sagewort increase. When compared to the Rhizomatous Wheatgrass-Needle and Thread-Blue Grama Plant Community (1.1), blue grama and threadleaf sedge increase significantly. The mid-grass has declined dramatically. Annual brome may invade this plant community. Annual production has decreased significantly. This plant community is resistant to change. The thick sod prevents other species from establishing. Often, a seed source is not readily available. Infiltration decreases as runoff increases. The hydrologic cycle is impaired. There is less than 10 percent bare ground.
Figure 13. Annual production by plant type (representative values) or group (midpoint values)
Table 7. Annual production by plant type
| Plant type | Low (lb/acre) |
Representative value (lb/acre) |
High (lb/acre) |
|---|---|---|---|
| Grass/Grasslike | 275 | 495 | 710 |
| Forb | 25 | 75 | 125 |
| Shrub/Vine | 0 | 30 | 65 |
| Total | 300 | 600 | 900 |
Figure 14. Plant community growth curve (percent production by month). NE6405, Pine Ridge/Badlands, warm-season dominant. Warm-season dominant.
| Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec |
|---|---|---|---|---|---|---|---|---|---|---|---|
| J | F | M | A | M | J | J | A | S | O | N | D |
| 3 | 7 | 15 | 20 | 30 | 15 | 5 | 5 |
State 3
Early Seral State
The Early Seral State is the result of very heavy, disturbance such as rodent activity or livestock concentration areas. Extended periods of drought accompanied by heavy grazing can also push an ‘At Risk’ Plant Community Phase to this State. In most cases, this phase is dominated by pioneer perennial and annual grass and forb species. The percentage of bare ground is also much higher than on any other plant community phase in this ecological site.
Community 3.1
Threeawn/Annuals
This plant community developed with frequent and severe defoliation and/or heavy disturbance. The plant composition is made up of annuals with a few species of perennial forbs and grasses that are tolerant to frequent and severe defoliation. Grasses and grass-like species include threeawn, annual brome, blue grama, threadleaf sedge, sixweeks fescue, and scattered patches of buffalograss. The dominant perennial forbs include curlycup gumweed, hairy false goldenaster, and verbena. Broom snakeweed, fringed sagewort, cactus, and tarragon (green sagewort) increase. This plant community is also susceptible to invasion of Canada thistle and other non-native species because of the relatively high percentage of bare ground. Compared to the Rhizomatous Wheatgrass-Needle and Thread-Blue Grama Plant Community (1.1), all perennial plant species have been greatly reduced with only remnants of the most grazing-tolerant species present. Desirable native plant (i.e., those plants that maintain a healthy soil and plant community) diversity is low. This plant community is resistant to change because of the loss of plant diversity and overall soil disturbance. The hazards of wind and water erosion are high due to increased bare ground and the shallow-rooted herbaceous plant community. Loss of root mass and rodent-related soil disturbance has altered the hydrology.
Figure 15. Annual production by plant type (representative values) or group (midpoint values)
Table 8. Annual production by plant type
| Plant type | Low (lb/acre) |
Representative value (lb/acre) |
High (lb/acre) |
|---|---|---|---|
| Grass/Grasslike | 220 | 405 | 590 |
| Forb | 55 | 120 | 185 |
| Shrub/Vine | 25 | 75 | 125 |
| Total | 300 | 600 | 900 |
Figure 16. Plant community growth curve (percent production by month). NE6403, Pine Ridge/Badlands, cool-season/warm-season co-dominant. Cool-season, warm-season co-dominant.
| Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec |
|---|---|---|---|---|---|---|---|---|---|---|---|
| J | F | M | A | M | J | J | A | S | O | N | D |
| 5 | 10 | 20 | 25 | 20 | 10 | 5 | 5 |
State 4
Native/Invaded State
The Native/Invaded State has been invaded by field brome, cheatgrass, crested wheatgrass, smooth brome, and/or Kentucky bluegrass, but not at the levels at which the plant communities are dominated by these species. Long-term non-use, in combination with above-average precipitation, may transition a Native/Invaded plant community to a plant community phase that consists predominantly of non-native cool-season grasses. This scenario has been observed on this ecological site in small acreage fields, but not on larger tracts of land in this portion of MLRA 64. This transition can be observed in the northern portion of the MLRA, and in adjacent MLRAs. Once these species are established, it is unlikely that an invaded plant community can be returned to the Reference State (1.0). Cheatgrass and field brome will always be present in these plant communities, but during years with very wet falls and early springs, these two species can make up a significant percentage of the total annual production. As the seed bank of these species grows, the more difficult they will be to control.
Community 4.1
Rhizomatous Wheatgrass-Needle and Thread-Non-Native Cool-Season Grasses
This plant community phase is similar to the Rhizomatous Wheatgrass-Needle and Thread-Blue Grama Plant Community (1.1), but it also contains minor amounts of non-native invasive grass species such as cheatgrass, field brome, crested wheatgrass, and/or smooth brome (up to about 15 percent by air-dry weight). The potential vegetation consists of about 80 percent grasses, 5 percent grass-like plants, 10 percent forbs, and 5 percent shrubs. The community is dominated by cool-season grasses. The major grasses include rhizomatous wheatgrass, needle and thread, and blue grama. Other grass or grass-like species include prairie Junegrass, Sandberg bluegrass, buffalograss. Cheatgrass and field brome will always be present in this plant community, but during years with very wet falls and early springs, these two species can make up make up a significant percentage of the total annual production. As the seed bank of these species grows the more difficult they will be to control. This plant community is resilient and well adapted to the Northern Great Plains climatic conditions. The diversity in plant species allows for high tolerance to drought. This is a sustainable plant community regarding site/soil stability, watershed function, and biologic integrity.
Figure 17. Annual production by plant type (representative values) or group (midpoint values)
Table 9. Annual production by plant type
| Plant type | Low (lb/acre) |
Representative value (lb/acre) |
High (lb/acre) |
|---|---|---|---|
| Grass/Grasslike | 915 | 1575 | 2130 |
| Forb | 85 | 135 | 185 |
| Shrub/Vine | 0 | 90 | 185 |
| Total | 1000 | 1800 | 2500 |
Figure 18. Plant community growth curve (percent production by month). NE6401, Pine Ridge/Badlands, cool-season dominant. Cool-season dominant.
| Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec |
|---|---|---|---|---|---|---|---|---|---|---|---|
| J | F | M | A | M | J | J | A | S | O | N | D |
| 5 | 15 | 28 | 30 | 10 | 2 | 5 | 5 |
Community 4.2
Blue Grama-Rhizomatous Wheatgrass-Annual and/or Perennial Non-Native Cool-Season Grasses
This plant community develops from continuous seasonal or continuous season-long grazing, or non-use and no fire, and the invasion of non-native cool-season grasses. Species composition is made up of 85 percent warm-season shortgrasses and cool-season mid-grasses, 10 percent forbs, and approximately 5 percent shrubs. The dominant grasses and grass-like species include blue grama, buffalograss, threadleaf sedge, rhizomatous wheatgrass, prairie Junegrass, Sandberg bluegrass, cheatgrass, and field brome. Under long-term non-use, crested wheatgrass, smooth brome, and/or Kentucky bluegrass may invade. Forbs commonly found on this plant community include cudweed sagewort, scarlet globemallow, and Cuman ragweed. Under proper management, this plant community is stable. The soil erosion is low to moderate. Infiltration and runoff are moderate.
Figure 19. Annual production by plant type (representative values) or group (midpoint values)
Table 10. Annual production by plant type
| Plant type | Low (lb/acre) |
Representative value (lb/acre) |
High (lb/acre) |
|---|---|---|---|
| Grass/Grasslike | 745 | 1020 | 1290 |
| Forb | 55 | 120 | 185 |
| Shrub/Vine | 0 | 60 | 125 |
| Total | 800 | 1200 | 1600 |
Figure 20. Plant community growth curve (percent production by month). NE6403, Pine Ridge/Badlands, cool-season/warm-season co-dominant. Cool-season, warm-season co-dominant.
| Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec |
|---|---|---|---|---|---|---|---|---|---|---|---|
| J | F | M | A | M | J | J | A | S | O | N | D |
| 5 | 10 | 20 | 25 | 20 | 10 | 5 | 5 |
Pathway 4.1A
Community 4.1 to 4.2
Continuous seasonal grazing during the active growing period of cool-season plants, or continuous season-long grazing and drought will lead to Plant Community Phase (4.2).
Pathway 4.2A
Community 4.2 to 4.1
Prescribed grazing that allows for adequate plant recovery periods and normal precipitation patterns following drought will move this plant community toward the Rhizomatous Wheatgrass-Needle and Thread-Non-Native Cool-Season Grasses Plant Community Phase (4.1). Prescribed burning and/or chemical herbaceous weed control may be management options to help accelerate the change.
Conservation practices
| Prescribed Burning | |
|---|---|
| Prescribed Grazing | |
| Herbaceous Weed Control |
State 5
Renovated (R) Sod State
The Renovated (R) Sod State has been invaded by field brome, cheatgrass, crested wheatgrass, smooth brome, and/or Kentucky bluegrass, but not at the levels at which the plant communities are dominated by these species. Long-term non-use, in combination with above-average precipitation, may transition a Native/Invaded plant community to a plant community phase that is predominantly non-native cool-season grasses. This scenario has been observed on this ecological site in small acreage fields but not on larger tracts of land in this portion of MLRA 64. This transition can be observed in the northern portion of the MLRA and in adjacent MLRAs. Once these species are established it is unlikely that an invaded plant community can be returned to the Reference State (1.0). Cheatgrass and field brome will always be present in these plant communities, but during years with very wet falls and early springs, these two species can make up a significant percentage of the total annual production. As the seed bank of these species grows, the more difficult they will be to control.
Community 5.1
(R) Rhizomatous Wheatgrass-Needle and Thread-Blue Grama-Buffalograss
With proper management after renovation (R), this plant community will have similar plant composition and growth curve characteristics as the Reference Plant Community (1.1), however, the production will likely be slightly higher, depending on the degree of alteration. Proper grazing management must be implemented to maintain this plant community.
Community 5.2
(R) Blue Grama-Buffalograss/Threadleaf Sedge
This plant community will be similar to the Blue Grama-Buffalograss Sod Plant Community (2.1) in most respects. The main difference is the microrelief created by the renovation. Depending on the renovation technique, the microrelief can remain on the landscape for many decades, making vehicular travel across the landscape uncomfortable, if not extremely difficult. The forage production potential of a shortgrass plant community can be quickly improved through mechanical renovation. Mechanical renovation creates microrelief through practices including contour furrowing, contour pitting, terracing, chiseling, and disking. The purpose of the practice is to mechanically break up a sod-bound vegetative condition, or compacted soils. Renovation can restore hydrologic function by increasing infiltration and decreasing runoff. These factors favor cool-season species such as rhizomatous wheatgrasses, needle and thread, green needlegrass, and a variety of forbs. Mechanical renovation may not be economically feasible and if the management activities that created the plant community are not changed, the renovation will not be successful.
Pathway 5.1A
Community 5.1 to 5.2
Continuous season-long grazing, or continuous seasonal grazing, or heavy grazing in combination with drought will shift this plant community to the Renovated (R) Blue Grama-Buffalograss Sod Plant Community (5.2).
Pathway 5.2A
Community 5.2 to 5.1
This plant community can be returned to the (R) Rhizomatous Wheatgrass-Needle and Thread-Blue Grama-Buffalograss Plant Community (5.1) through another mechanical renovation treatment and possibly seeding, followed by long-term prescribed grazing and normal precipitation patterns. The second mechanical treatment may make travel across the landscape very difficult for vehicles and livestock.
Conservation practices
| Grazing Land Mechanical Treatment | |
|---|---|
| Prescribed Grazing |
State 6
Disturbed State
The Disturbed State can be transitioned to from any Plant Community. It is the result of prior cultivation and abandonment of cropland (go-back), or tillage and seeding to a forage crop, or extensive soil disturbance and/or soil erosion. The two separate vegetative plant communities are highly variable in nature. They are derived through different management scenarios, and are not related successionally. Infiltration, runoff, and soil erosion varies depending on the vegetation present on the site.
Community 6.1
Go-Back
The Go-Back Plant Community can be reached whenever severe mechanical disturbance occurs (e.g., tilled and abandoned land). During the early successional stages, the species that mainly dominate are annual grasses and forbs, later replaced by both native and introduced perennials. The vegetation on this site vary greatly, sometimes being dominated by threeawn, annual brome, crested wheatgrass, dropseed, broom snakeweed, verbena, sweet clover, mullein, and non-native thistles. Other plants that commonly occur on the site include western wheatgrass, deathcamas, prickly lettuce, mare’s-tail, kochia, foxtail, and sunflowers. Bare ground is prevalent due to the loss of organic matter and lower overall soil health.
Community 6.2
Seeded
The Seeded Plant Community consists of those areas seeded to pubescent or intermediate wheatgrass, alfalfa, crested wheatgrass, or other introduced forage species. For adapted species and expected production, refer to the USDA-NRCS eFOTG for the appropriate Forage Suitability Group description.
Transition T1A
State 1 to 2
Continuous seasonal grazing or continuous season-long grazing, or heavy grazing during extended period of drought will transition this plant community (1.2) to the Shortgrass State (2.0). Once this site becomes sod-bound there will be a loss of hydrologic function resulting in increased run-off and less infiltration.
Transition T1C
State 1 to 3
Frequent and severe defoliation, or heavy disturbance causing a loss of hydrologic function. Examples include livestock concentration areas (feeding), prairie dog towns, small horse pastures, etc. Runoff will increase, and infiltration will decrease. These disturbances will cause a transition to the Early Seral State (3.0).
Transition T1B
State 1 to 4
Continuous season-long grazing, or continuous seasonal grazing, or non-use and no fire, and invasion of non-native cool-season grasses will cause a transition to the Native/Invaded State (4.0).
Transition T7A
State 1 to 6
Heavy disturbance including soil erosion, tillage, abandonment of cropland, or seeding to improved pasture species will result in a transition to the Disturbed State (6.0).
Restoration pathway R2A
State 2 to 1
Long-term prescribed grazing may potentially convert the plant community to the Blue Grama-Rhizomatous Wheatgrass/Threadleaf Sedge Plant Community (1.2), assuming an adequate seed/vegetative source is present. A return to normal precipitation patterns will help to expedite this transition. This could require significant time and input to achieve and, in the end, may not meet management objectives.
Conservation practices
| Prescribed Grazing |
|---|
Transition T2A
State 2 to 3
Frequent and severe defoliation and/or heavy disturbance including livestock concentration areas (feeding), prairie dog towns, small horse pastures, etc. will cause a transition to the Early Seral State (3.0). Runoff will increase, and infiltration will decrease.
Transition T2B
State 2 to 4
Removal of management-induced disturbance, invasion of non-native cool-season grasses, and long-term prescribed grazing may result in a transition to the Native/Invaded State (4.0). A return to normal precipitation patterns will help expedite this transition. This could require significant time and input to achieve and, in the end, may not meet management objectives.
Transition T2C
State 2 to 5
Mechanical renovation will move this plant community to the Renovated (R) Sod State (5.0). Proper grazing management must be included in order to derive the benefits of renovation.
Transition T7A
State 2 to 6
Heavy disturbance including soil erosion, tillage, abandonment of cropland, or seeding to improved pasture species will result in a transition to the Disturbed State (6.0).
Restoration pathway R3A
State 3 to 2
Removal of the management-induced disturbance, in association with long-term prescribed grazing and favorable climatic conditions, may allow for adequate plant recovery and a transition to the Shortgrass Sod State (2.0). Periods of non-use or deferment may be a management option to facilitate this movement. This transition will not be rapid and may not meet management objectives.
Conservation practices
| Prescribed Grazing |
|---|
Transition T3A
State 3 to 5
Mechanical renovation, and possibly seeding, will move this plant community to the Renovated (R) Sod State (5.0). Proper grazing management must be included in order to derive the benefits of renovation.
Transition T7A
State 3 to 6
Heavy disturbance including soil erosion, tillage, abandonment of cropland, or seeding to improved pasture species will result in a transition to the Disturbed State (6.0).
Transition T4A
State 4 to 3
Continuous season-long grazing or heavy grazing during extended period of drought will transition this plant community to the Shortgrass State (3.0). Once this site becomes sod-bound there will be a loss of hydrologic function, resulting in increased runoff and less infiltration.
Transition T7A
State 4 to 6
Heavy disturbance including soil erosion, tillage, abandonment of cropland, or seeding to improved pasture species will result in a transition to the Disturbed State (6.0).
Transition T5B
State 5 to 3
Frequent and severe defoliation, and/or heavy disturbance including livestock concentration areas (feeding), prairie dog towns, small horse pastures, etc. will cause a transition to the Early Seral State (3.0). Runoff will increase and infiltration will decrease.
Transition T5A
State 5 to 4
Continuous season-long grazing, or long-term light grazing, or non-use and no fire, and invasion of non-native cool-season grasses will cause a transition to the Native/Invaded State (4.0).
Transition T7A
State 5 to 6
Heavy disturbance including soil erosion, tillage, abandonment of cropland, or seeding to improved pasture species will result in a transition to the Disturbed State (6.0).
Additional community tables
Table 11. Community 1.1 plant community composition
| Group | Common name | Symbol | Scientific name | Annual production (lb/acre) | Foliar cover (%) | |
|---|---|---|---|---|---|---|
|
Grass/Grasslike
|
||||||
| 1 | Rhizomatous Wheatgrass | 360–540 | ||||
| western wheatgrass | PASM | Pascopyrum smithii | 360–540 | – | ||
| thickspike wheatgrass | ELLAL | Elymus lanceolatus ssp. lanceolatus | 90–250 | – | ||
| 2 | Cool-Season Bunchgrasses | 270–450 | ||||
| needle and thread | HECOC8 | Hesperostipa comata ssp. comata | 270–360 | – | ||
| green needlegrass | NAVI4 | Nassella viridula | 90–180 | – | ||
| 3 | Warm Season Shortgrasses | 90–270 | ||||
| blue grama | BOGR2 | Bouteloua gracilis | 90–270 | – | ||
| buffalograss | BODA2 | Bouteloua dactyloides | 0–90 | – | ||
| 4 | Native Grasses and Grass-likes | 90–360 | ||||
| threadleaf sedge | CAFI | Carex filifolia | 90–180 | – | ||
| big bluestem | ANGE | Andropogon gerardii | 0–90 | – | ||
| sideoats grama | BOCU | Bouteloua curtipendula | 0–90 | – | ||
| little bluestem | SCSC | Schizachyrium scoparium | 0–90 | – | ||
| prairie Junegrass | KOMA | Koeleria macrantha | 0–36 | – | ||
|
Forb
|
||||||
| 6 | Forbs | 90–180 | ||||
| scurfpea | PSORA2 | Psoralidium | 0–36 | – | ||
| white sagebrush | ARLU | Artemisia ludoviciana | 0–36 | – | ||
| milkvetch | ASTRA | Astragalus | 0–36 | – | ||
| Cuman ragweed | AMPS | Ambrosia psilostachya | 0–36 | – | ||
| pussytoes | ANTEN | Antennaria | 0–36 | – | ||
| blacksamson echinacea | ECAN2 | Echinacea angustifolia | 0–36 | – | ||
| hairy false goldenaster | HEVI4 | Heterotheca villosa | 0–36 | – | ||
| bush morning-glory | IPLE | Ipomoea leptophylla | 0–36 | – | ||
| goldenrod | SOLID | Solidago | 0–36 | – | ||
| scarlet globemallow | SPCO | Sphaeralcea coccinea | 0–36 | – | ||
| white heath aster | SYER | Symphyotrichum ericoides | 0–18 | – | ||
| vervain | VERBE | Verbena | 0–18 | – | ||
| dotted blazing star | LIPU | Liatris punctata | 0–18 | – | ||
| rush skeletonplant | LYJU | Lygodesmia juncea | 0–18 | – | ||
| lacy tansyaster | MAPI | Machaeranthera pinnatifida | 0–18 | – | ||
| beardtongue | PENST | Penstemon | 0–18 | – | ||
| false boneset | BREU | Brickellia eupatorioides | 0–18 | – | ||
| corn gromwell | BUAR3 | Buglossoides arvensis | 0–18 | – | ||
| upright prairie coneflower | RACO3 | Ratibida columnifera | 0–18 | – | ||
| stiff sunflower | HEPA19 | Helianthus pauciflorus | 0–18 | – | ||
| tarragon | ARDR4 | Artemisia dracunculus | 0–18 | – | ||
| scarlet beeblossom | GACO5 | Gaura coccinea | 0–18 | – | ||
|
Shrub/Vine
|
||||||
| 7 | Shrubs | 0–180 | ||||
| leadplant | AMCA6 | Amorpha canescens | 0–90 | – | ||
| rose | ROSA5 | Rosa | 0–90 | – | ||
| Wyoming big sagebrush | ARTRW8 | Artemisia tridentata ssp. wyomingensis | 0–65 | – | ||
| winterfat | KRLA2 | Krascheninnikovia lanata | 0–65 | – | ||
| prairie sagewort | ARFR4 | Artemisia frigida | 0–36 | – | ||
| snowberry | SYMPH | Symphoricarpos | 0–36 | – | ||
| soapweed yucca | YUGL | Yucca glauca | 0–36 | – | ||
| pricklypear | OPUNT | Opuntia | 0–18 | – | ||
Table 12. Community 1.2 plant community composition
| Group | Common name | Symbol | Scientific name | Annual production (lb/acre) | Foliar cover (%) | |
|---|---|---|---|---|---|---|
|
Grass/Grasslike
|
||||||
| 1 | Rhizomatous Wheatgrass | 60–240 | ||||
| western wheatgrass | PASM | Pascopyrum smithii | 60–240 | – | ||
| thickspike wheatgrass | ELLAL | Elymus lanceolatus ssp. lanceolatus | 0–90 | – | ||
| 2 | Cool-Season Bunchgrasses | 24–120 | ||||
| needle and thread | HECOC8 | Hesperostipa comata ssp. comata | 24–120 | – | ||
| green needlegrass | NAVI4 | Nassella viridula | 0–60 | – | ||
| 3 | Warm-Season Shortgrasses | 240–480 | ||||
| blue grama | BOGR2 | Bouteloua gracilis | 120–360 | – | ||
| buffalograss | BODA2 | Bouteloua dactyloides | 120–180 | – | ||
| 4 | Native Grasses and Grass-likes | 60–240 | ||||
| threadleaf sedge | CAFI | Carex filifolia | 60–120 | – | ||
| sand dropseed | SPCR | Sporobolus cryptandrus | 0–60 | – | ||
| prairie Junegrass | KOMA | Koeleria macrantha | 12–48 | – | ||
| sideoats grama | BOCU | Bouteloua curtipendula | 0–36 | – | ||
| plains muhly | MUCU3 | Muhlenbergia cuspidata | 0–24 | – | ||
| Sandberg bluegrass | POSE | Poa secunda | 0–24 | – | ||
| little bluestem | SCSC | Schizachyrium scoparium | 0–24 | – | ||
| big bluestem | ANGE | Andropogon gerardii | 0–24 | – | ||
| threeawn | ARIST | Aristida | 0–24 | – | ||
| sixweeks fescue | VUOC | Vulpia octoflora | 0–12 | – | ||
| 5 | Non-Native Grasses | 0–60 | ||||
| field brome | BRAR5 | Bromus arvensis | 0–60 | – | ||
| cheatgrass | BRTE | Bromus tectorum | 0–60 | – | ||
| Kentucky bluegrass | POPR | Poa pratensis | 0–60 | – | ||
|
Forb
|
||||||
| 6 | Forbs | 60–180 | ||||
| Cuman ragweed | AMPS | Ambrosia psilostachya | 0–120 | – | ||
| sweetclover | MELIL | Melilotus | 0–60 | – | ||
| vervain | VERBE | Verbena | 0–60 | – | ||
| tarragon | ARDR4 | Artemisia dracunculus | 0–36 | – | ||
| white sagebrush | ARLU | Artemisia ludoviciana | 0–36 | – | ||
| milkvetch | ASTRA | Astragalus | 0–24 | – | ||
| pussytoes | ANTEN | Antennaria | 0–24 | – | ||
| curlycup gumweed | GRSQ | Grindelia squarrosa | 0–24 | – | ||
| scurfpea | PSORA2 | Psoralidium | 0–24 | – | ||
| hairy false goldenaster | HEVI4 | Heterotheca villosa | 0–24 | – | ||
| goatsbeard | TRAGO | Tragopogon | 0–24 | – | ||
| scarlet globemallow | SPCO | Sphaeralcea coccinea | 0–24 | – | ||
| white heath aster | SYER | Symphyotrichum ericoides | 0–12 | – | ||
| bush morning-glory | IPLE | Ipomoea leptophylla | 0–12 | – | ||
| dotted blazing star | LIPU | Liatris punctata | 0–12 | – | ||
| rush skeletonplant | LYJU | Lygodesmia juncea | 0–12 | – | ||
| lacy tansyaster | MAPI | Machaeranthera pinnatifida | 0–12 | – | ||
| upright prairie coneflower | RACO3 | Ratibida columnifera | 0–12 | – | ||
| goldenrod | SOLID | Solidago | 0–12 | – | ||
| beardtongue | PENST | Penstemon | 0–12 | – | ||
| stiff sunflower | HEPA19 | Helianthus pauciflorus | 0–12 | – | ||
| false boneset | BREU | Brickellia eupatorioides | 0–12 | – | ||
| corn gromwell | BUAR3 | Buglossoides arvensis | 0–12 | – | ||
| blacksamson echinacea | ECAN2 | Echinacea angustifolia | 0–12 | – | ||
| scarlet beeblossom | GACO5 | Gaura coccinea | 0–12 | – | ||
|
Shrub/Vine
|
||||||
| 7 | Shrubs | 0–120 | ||||
| prairie sagewort | ARFR4 | Artemisia frigida | 0–60 | – | ||
| broom snakeweed | GUSA2 | Gutierrezia sarothrae | 0–60 | – | ||
| pricklypear | OPUNT | Opuntia | 0–60 | – | ||
| snowberry | SYMPH | Symphoricarpos | 0–60 | – | ||
| soapweed yucca | YUGL | Yucca glauca | 0–60 | – | ||
| winterfat | KRLA2 | Krascheninnikovia lanata | 0–45 | – | ||
| Wyoming big sagebrush | ARTRW8 | Artemisia tridentata ssp. wyomingensis | 0–45 | – | ||
| rose | ROSA5 | Rosa | 0–24 | – | ||
| leadplant | AMCA6 | Amorpha canescens | 0–12 | – | ||
Table 13. Community 2.1 plant community composition
| Group | Common name | Symbol | Scientific name | Annual production (lb/acre) | Foliar cover (%) | |
|---|---|---|---|---|---|---|
|
Grass/Grasslike
|
||||||
| 1 | Rhizomatous Wheatgrass | 6–30 | ||||
| western wheatgrass | PASM | Pascopyrum smithii | 6–30 | – | ||
| thickspike wheatgrass | ELLAL | Elymus lanceolatus ssp. lanceolatus | 0–10 | – | ||
| 2 | Cool-Season Bunchgrasses | 0–12 | ||||
| needle and thread | HECOC8 | Hesperostipa comata ssp. comata | 0–12 | – | ||
| 3 | Warm Season Shortgrasses | 240–390 | ||||
| blue grama | BOGR2 | Bouteloua gracilis | 120–300 | – | ||
| buffalograss | BODA2 | Bouteloua dactyloides | 90–150 | – | ||
| 4 | Native Grasses and Grass-likes | 60–120 | ||||
| threeawn | ARIST | Aristida | 6–30 | – | ||
| threadleaf sedge | CAFI | Carex filifolia | 6–30 | – | ||
| prairie Junegrass | KOMA | Koeleria macrantha | 6–30 | – | ||
| sand dropseed | SPCR | Sporobolus cryptandrus | 0–30 | – | ||
| sixweeks fescue | VUOC | Vulpia octoflora | 0–12 | – | ||
| 5 | Non-Native Grasses | 6–30 | ||||
| cheatgrass | BRTE | Bromus tectorum | 6–30 | – | ||
| field brome | BRAR5 | Bromus arvensis | 0–20 | – | ||
| Kentucky bluegrass | POPR | Poa pratensis | 0–6 | – | ||
|
Forb
|
||||||
| 6 | Forbs | 30–120 | ||||
| Cuman ragweed | AMPS | Ambrosia psilostachya | 0–60 | – | ||
| tarragon | ARDR4 | Artemisia dracunculus | 0–30 | – | ||
| white sagebrush | ARLU | Artemisia ludoviciana | 0–30 | – | ||
| sweetclover | MELIL | Melilotus | 0–30 | – | ||
| scurfpea | PSORA2 | Psoralidium | 0–30 | – | ||
| curlycup gumweed | GRSQ | Grindelia squarrosa | 0–30 | – | ||
| vervain | VERBE | Verbena | 0–30 | – | ||
| hairy false goldenaster | HEVI4 | Heterotheca villosa | 0–18 | – | ||
| goatsbeard | TRAGO | Tragopogon | 0–12 | – | ||
| lacy tansyaster | MAPI | Machaeranthera pinnatifida | 0–6 | – | ||
| scarlet globemallow | SPCO | Sphaeralcea coccinea | 0–6 | – | ||
| white heath aster | SYER | Symphyotrichum ericoides | 0–6 | – | ||
| milkvetch | ASTRA | Astragalus | 0–6 | – | ||
| scarlet beeblossom | GACO5 | Gaura coccinea | 0–6 | – | ||
|
Shrub/Vine
|
||||||
| 7 | Shrubs | 0–60 | ||||
| prairie sagewort | ARFR4 | Artemisia frigida | 0–30 | – | ||
| broom snakeweed | GUSA2 | Gutierrezia sarothrae | 0–30 | – | ||
| pricklypear | OPUNT | Opuntia | 0–30 | – | ||
| soapweed yucca | YUGL | Yucca glauca | 0–30 | – | ||
| Wyoming big sagebrush | ARTRW8 | Artemisia tridentata ssp. wyomingensis | 0–25 | – | ||
| winterfat | KRLA2 | Krascheninnikovia lanata | 0–10 | – | ||
Table 14. Community 3.1 plant community composition
| Group | Common name | Symbol | Scientific name | Annual production (lb/acre) | Foliar cover (%) | |
|---|---|---|---|---|---|---|
|
Grass/Grasslike
|
||||||
| 1 | Rhizomatous Wheatgrass | 0–30 | ||||
| western wheatgrass | PASM | Pascopyrum smithii | 0–30 | – | ||
| thickspike wheatgrass | ELLAL | Elymus lanceolatus ssp. lanceolatus | 0–10 | – | ||
| 3 | Warm Season Shortgrasses | 0–60 | ||||
| blue grama | BOGR2 | Bouteloua gracilis | 0–60 | – | ||
| buffalograss | BODA2 | Bouteloua dactyloides | 0–18 | – | ||
| 4 | Native Grasses and Grass-likes | 240–450 | ||||
| threeawn | ARIST | Aristida | 60–210 | – | ||
| prairie Junegrass | KOMA | Koeleria macrantha | 0–30 | – | ||
| sixweeks fescue | VUOC | Vulpia octoflora | 0–30 | – | ||
| threadleaf sedge | CAFI | Carex filifolia | 0–18 | – | ||
| sand dropseed | SPCR | Sporobolus cryptandrus | 0–6 | – | ||
| 5 | Non-Native Grasses | 6–60 | ||||
| cheatgrass | BRTE | Bromus tectorum | 6–60 | – | ||
| field brome | BRAR5 | Bromus arvensis | 0–35 | – | ||
|
Forb
|
||||||
| 6 | Forbs | 60–180 | ||||
| thistle | CIRSI | Cirsium | 0–90 | – | ||
| vervain | VERBE | Verbena | 0–30 | – | ||
| Cuman ragweed | AMPS | Ambrosia psilostachya | 0–30 | – | ||
| pussytoes | ANTEN | Antennaria | 0–30 | – | ||
| white sagebrush | ARLU | Artemisia ludoviciana | 0–18 | – | ||
| milkvetch | ASTRA | Astragalus | 0–6 | – | ||
| tarragon | ARDR4 | Artemisia dracunculus | 0–6 | – | ||
| curlycup gumweed | GRSQ | Grindelia squarrosa | 0–6 | – | ||
|
Shrub/Vine
|
||||||
| 7 | Shrubs | 30–120 | ||||
| prairie sagewort | ARFR4 | Artemisia frigida | 12–90 | – | ||
| broom snakeweed | GUSA2 | Gutierrezia sarothrae | 6–60 | – | ||
| pricklypear | OPUNT | Opuntia | 6–60 | – | ||
Interpretations
Animal community
Wildlife Interpretations:
MLRA 64 is in the drier areas of a northern mixed-grass prairie ecosystem in which sagebrush steppes to the west yield to grassland steppes to the east. Prior to European settlement, this MLRA consisted of diverse grassland and shrubland habitats interspersed with varying densities of depressional, instream wetlands and woody riparian corridors. These habitats provided critical life cycle components for many users. Many species of grassland birds, small mammals, reptiles, and amphibians and herds of roaming bison, elk, and pronghorn were among the inhabitants adapted to this semi-arid region. Roaming herbivores, as well as several species of small mammals and insects, were the primary consumers linking the grassland resources to large predators, such as the wolf, mountain lion, and grizzly bear, and to smaller carnivores, such as the coyote, bobcat, fox, and raptors. The prairie dog was once abundant and remains a keystone species within its range. The black-footed ferret, burrowing owl, ferruginous hawk, mountain plover, and swift fox are associated with prairie dog complexes.
Historically, the northern mixed-grass prairie was a disturbance-driven ecosystem in which fire, herbivory, and climate functioned as the primary disturbance factors, either singly or in combination. Following European settlement, livestock grazing, cropland conversion, elimination of fire, energy development, and other anthropogenic factors influenced species composition and abundance. Introduced and invasive species further affected plant and animal communities. The bison was a historical keystone species but has been extirpated in this area as a free-ranging herbivore. The loss of the bison and the reduction of prairie dog populations and fire as ecological drivers greatly influenced the character of the remaining native plant communities and altered wildlife habitats. Human development reduced habitat quality for area-sensitive species.
Within MLRA 64, the Loamy 14-17” PZ ecological site provides upland grassland cover with an associated forb, shrub, and tree component. It was typically part of an expansive grassland landscape that included combinations of Badlands, Thin Breaks, Clayey, Claypan, Dense Clay, Loamy, Saline, Sandy, Shallow, Overflow, Subirrigated, and Terrace ecological sites. This site provided habitat for species that require unfragmented grassland. Important habitat features and components found commonly or exclusively on this site may include sharp-tailed grouse leks; upland nesting habitat for grassland birds, forbs and insects for brood habitat; and a forage source for small and large herbivores. Many grassland- and shrub steppe-nesting bird populations are declining. Species extirpated in MLRA 64 include free-ranging American bison, grizzly bear, gray wolf, black-footed ferret, mountain plover, Rocky Mountain locust, and swift fox.
The majority of the Loamy 14-17” PZ site remains intact and provides increasingly important habitat for grassland- and shrub steppe-nesting birds, small rodents, coyote, and a variety of reptiles, amphibians, and insects. Invasive species such as annual brome grasses, including cheatgrass and field brome, have impacted the biological integrity of the site for some grassland birds. Changes in historic fire regime and domestic grazing have impacted the forb/shrub/grass percentages.
Rhizomatous Wheatgrass-Needle and Thread Blue Grama Plant Community (1.1): The predominance of grasses in this vegetative state favors grazers and mixed-feeders, such as bison and antelope. Suitable thermal and escape cover for deer may be limited due to the low quantities of woody plants; however, topographical variations could provide some escape cover. Portions along woody vegetative states may provide brood-rearing and foraging areas for sage grouse, as well as lek sites. Other birds that would frequent this plant community include Western meadowlarks, horned larks, and golden eagles. Many grasslands obligate small mammals would occur here. Swift fox and a number of non-game grassland bird species will do better in some of the other plant communities on this site that have less height or density of the cool-season grasses.
Blue Grama-Rhizomatous Wheatgrass/Threadleaf Sedge Plant Community (1.2): Wildlife, such as shortgrass prairie bird species and swift fox would benefit from the reduced cover. Upland game bird habitat quality would decline. The diversity of this plant community is still high enough to support many of the species that would be present with the Rhizomatous Wheatgrass-Needle and Thread-Blue Grama Plant Community.
Blue Grama/Threadleaf Sedge Plant Community (2.1): This plant community provides limited foraging for antelope and other grazers. It may be used as a foraging site by sage grouse if proximal to woody cover and the Rhizomatous Wheatgrass-Needle and Thread-Blue Grama Plant Community. Generally, this plant community is not a target for wildlife habitat management. Wildlife, such as shortgrass prairie bird species and swift fox, would benefit from the reduced cover. Upland game bird habitat quality would decline.
Threeawn/Annuals Plant Community (3.1): Benefits to other wildlife are largely due to the subterranean structure created by the prairie dogs. It may be a desirable plant community if the goal is to provide habitat for burrowing owls or black-footed ferrets, or if maintenance of the dog town is desired for sport shooting purposes. Many native grassland wildlife species are directly or indirectly reliant on prairie dog habitat. As a result, this type of habitat is very important from an ecosystem management basis.
Grazing Interpretations:
The following list suggests annual, initial stocking rates for average growing conditions. These estimates are conservative and should be used only as guidelines in the initial stages of conservation planning. Commonly, the current plant composition does not entirely match any particular plant community (as described in this ecological site description). Therefore, a resource inventory is necessary to document plant composition and production. More accurate estimates of carrying capacity should eventually be calculated using the following stocking rate information along with animal preference data and actual stocking records, particularly when grazers other than cattle are involved. In consultation with the land manager, a more intensive grazing management program that results in improved harvest efficiencies and increased carrying capacity may be developed.
The following suggested initial stocking rates are based on 912 lb/acre (air-dry weight) per animal-unit-month (AUM) with a 25 percent harvest efficiency of preferred and desirable forage species (refer to USDA-NRCS, National Range and Pasture Handbook). An AUM is defined as the equivalent amount of forage required by a 1,000-pound cow, with or without calf, for one month.
Plant Community: Rhizomatous Wheatgrass-Needle and Thread-Blue Grama (1.1)
Average Production (lb/acre, air-dry): 1,800
Stocking Rate (AUM/acre): 0.49
Plant Community: Blue Grama-Rhizomatous Wheatgrass/Threadleaf Sedge (1.2)
Average Production (lb/acre, air-dry): 1,200
Stocking Rate (AUM/acre): 0.33
Plant Community: Blue Grama-Threadleaf Sedge (2.1)
Average Production (lb/acre, air-dry): 600
Stocking Rate (AUM/acre): 0.16
*Plant Community: Threeawn/Annuals (3.1)
Average Production (lb/acre, air-dry): 600
Stocking Rate (AUM/acre): Variable
Plant Community: Rhizomatous Wheatgrass-Needle and Thread-Non-Native Cool-Season Grasses (4.1)
Average Production (lb/acre, air-dry): 1,800
Stocking Rate (AUM/acre): 0.49
Plant Community: Blue Grama-Rhizomatous Wheatgrass-Annual and/or Perennial Non-Native Cool-Season Grasses (4.2)
Average Production (lb/acre, air-dry): 1,200
Stocking Rate (AUM/acre): 0.33
*Plant Community: (R) Rhizomatous Wheatgrass-Needle and Thread-Blue Grama-Buffalograss (5.1)
Average Production (lb/acre, air-dry): Variable
Stocking Rate (AUM/acre): Variable
*Plant Community: (R) Blue Grama-Buffalograss/Threadleaf Sedge (5.2)
Average Production (lbs./acre, air-dry): Variable
Stocking Rate (AUM/acre): Variable
Plant Community: All other plant communities identified in this document have variable annual production values and require onsite sampling to determine initial stocking rates.
* Total annual production and stocking rates are highly variable and require onsite sampling.
** Total onsite annual production may contain vegetation deemed undesirable or untargeted by the grazing animal. Therefore, AUM values may have been reduced to reflect only preferred or desirable forage species.
Grazing by domestic livestock is one of the major income-producing industries in the area. Rangeland in this area may provide yearlong forage for livestock. During the dormant period, the forage for livestock likely have insufficient protein to meet livestock requirements. Added protein allows ruminants to better utilize the energy stored in grazed plant materials. A forage quality test (either directly or through fecal sampling) should be used to determine the level of supplementation needed.
Hydrological functions
Water is the principal factor limiting forage production on this site. This site is dominated by soils in hydrologic group B, with localized areas in hydrologic group C. Infiltration and runoff potential for this site varies from moderate to high depending upon soil hydrologic group, slope, and ground cover. In many cases, areas with greater than 75 percent ground cover have the greatest potential for high infiltration and lower runoff. An example of an exception would be where shortgrasses form a strong sod and dominate the site. Dominance by blue grama, buffalograss, Kentucky bluegrass, and/or smooth brome will result in reduced infiltration and increased runoff. Areas where ground cover is less than 50 percent have the greatest potential to have reduced infiltration and higher runoff. Refer to the USDA-NRCS National Engineering Handbook, Part 630, for hydrologic soil groups, runoff quantities, and hydrologic curves.
Recreational uses
This site provides hunting, hiking, photography, bird watching, and other opportunities. The wide variety of plants that bloom from spring until fall have an aesthetic value that appeals to visitors.
Wood products
No appreciable wood products are present on the site.
Other products
Harvesting the seeds of native plants can provide additional income on this site.
Other information
Revision Notes: “Previously Approved” Provisional
This Provisional ecological site description (ESD) has passed Quality Control (QC) and Quality Assurance (QA) to ensure the it meets the 2014 NESH standards for a Provisional ecological site description.
This ESD is an updated “Previously Approved” ESD that represented a first-generation tier of documentation that, prior to the release of the 2014 National Ecological Site Handbook (NESH), met all requirements as an “Approved” ESD as laid out in the 1997 National Range and Pasture Handbook (NRPH). The document fully described the Reference State and Community Phase in the State-and-Transition model. All other alternative states are at least described in narrative form. The “Previously Approved” ESD has been field-tested for a minimum of five years and is a proven functional document for conservation planning. The “Previously Approved” ESD may not contain all tabular and narrative entries as required in the current “Approved” level of documentation, but it is expected that it will continue refinement toward an “Approved” status.
Site Development and Testing Plan
Future work, as described in an official project plan, is necessary to validate the information in this provisional ecological site description. The plan will include field activities for low-, medium-, and high-intensity sampling, soil correlations, and analysis of the data. Annual field reviews should be done by soil scientists and vegetation specialists. Final field review, peer review, quality control, and quality assurance reviews are required to produce the final document.
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: Stan Boltz, range management specialist (RMS), NRCS; Jill Epley, RMS, NRCS; Rick Peterson, RMS, NRCS; David Steffen, RMS, NRCS; Jeff Vander Wilt; RMS, NRCS; Phil Young, soil scientist, NRCS; and George Gamblin, RMS, NRCS.
Other references
Cleland, D.T., J.A. Freeouf, J.E. Keys, G.J. Nowacki, C.A. Carpenter, and W.H McNab. 2007. Ecological subregions: Sections and subsections of the conterminous United States. USDA Forest Service, General Technical Report WO-76D. https://www.fs.fed.us/research/publications/misc/73326-wo-gtr-76d-cleland2007.pdf (accessed 31 January 2019).
U.S. Environmental Protection Agency. 2018. EPA level III and level IV ecoregions of the conterminous United States. https://www.epa.gov/eco-research/level-iii-and-iv-ecoregions- conterminous-united-states (accessed 26 April 2018).
High Plains Regional Climate Center, University of Nebraska. 2018. http://www.hprcc.unl.edu/ (accessed 6 April 2018).
Steele, Ken, M.P. Fisher, and D.D. Steele. 2018. Fort Laramie and the Hartville Uplift. In: Geology of Wyoming. https://www.geowyo.com/fort-laramie--hartville-uplift.html (accessed 14 November 2018).
U.S. Department of Agriculture, Natural Resources Conservation Service. 2018. Electronic field office technical guide. https://efotg.sc.egov.usda.gov (accessed 12 April 2018).
Soil Survey Staff. 2018. Official soil series descriptions. USDA Natural Resources Conservation Service. https://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/home/?cid=nrcs142p2_053587 (accessed 12 April 2018).
Soil Survey Staff. 2018. Web Soil Survey. USDA Natural Resources Conservation Service. https://websoilsurvey.sc.egov.usda.gov/App/WebSoilSurvey.aspx (accessed 12 April 2018).
U.S. Department of Agriculture, Natural Resources Conservation Service. 2006. Land resource regions and major land resource areas of the United States, the Caribbean, and the Pacific Basin. Agriculture Handbook 296. https://www.nrcs.usda.gov/Internet/FSE_DOCUMENTS/nrcs142p2_050898.pdf (accessed 17 January 2018).
U.S. Department of Agriculture, Natural Resources Conservation Service. 2014. National ecological site handbook, 1st Ed. https://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/ref/?cid=nrcseprd1291232 (accessed 27 January 2018).
U.S. Department of Agriculture, Natural Resources Conservation Service. 2012. National engineering handbook, part 630. Hydrology chapters from e-Directives. https://directives.sc.egov.usda.gov/viewerFS.aspx?hid=21422 (accessed 17 January 2018).
U.S. Department of Agriculture, Natural Resources Conservation Service. 2018. Climate data. National Water and Climate Center. http://www.wcc.nrcs.usda.gov/ (accessed 12 April 2018).
U.S. Department of Agriculture, Natural Resources Conservation Service. 1997. National range and pasture handbook, rev. 1, 2003. https://www.nrcs.usda.gov/Internet/FSE_DOCUMENTS/stelprdb1043055.pdf (accessed 7 November 2018).
U.S. Department of Agriculture, Natural Resources Conservation Service. 2018. National Soil Information System, Information Technology Center. http://nasis.nrcs.usda.gov (accessed 7 November 2017).
U.S. Department of Agriculture, Natural Resources Conservation Service. 2018. PLANTS database. National Plant Data Team, Greensboro, NC. http://plants.usda.gov (accessed 12 April 2018).
Contributors
Rick L. Peterson
Stan C. Boltz
Approval
Suzanne Mayne-Kinney, 12/16/2024
Acknowledgments
This ecological site was reviewed and approved at the Approved Level by David Kraft, Regional ESS, Salina, KS on 1/23/2019.
Nondiscrimination Statement:
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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) | Stan Boltz, Mitch Faulkner, Emily Helms, John Hartung, Ryan Murray, George Gamblin, Rick Peterson, Nadine Bishop, Jeff Nichols |
|---|---|
| Contact for lead author | jeffrey.nichols@usda.gov |
| Date | 12/16/2024 |
| Approved by | Suzanne Mayne-Kinney |
| Approval date | |
| Composition (Indicators 10 and 12) based on | Annual Production |
Indicators
-
Number and extent of rills:
None. Rills should not be present. -
Presence of water flow patterns:
Typically, none. Water flow patterns may be present on slopes of 15 percent or greater. When present, they will be no longer than 2 to 4 inches (5 to 10 cm), less than 3 inches (7.5 cm) wide, and discontinuous. Water flow patterns, when present, are often associated with animal activity. -
Number and height of erosional pedestals or terracettes:
None. Pedestals or terracettes should not be present. -
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
Bare ground is typically 5 to 10 percent or less and bare ground patches are less than 2 inches (5 cm) in diameter. -
Number of gullies and erosion associated with gullies:
None. Gullies should not be present. -
Extent of wind scoured, blowouts and/or depositional areas:
None. Wind scoured areas and depositional areas should not be present. -
Amount of litter movement (describe size and distance expected to travel):
Litter should fall in place. Slight amount of movement (less than 6 inches or 15 cm) of fine litter from water is possible, but not normal. Litter movement from wind is not expected. -
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
Soil stability ratings should typically be 5 to 6, normally 6. Surface organic matter adheres to the soil surface. Soil surface fragments will typically retain structure indefinitely when dipped in distilled water. -
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
A-horizon should be 5 to 25 inches (12.5 to 63.5 cm) thick. Colors range from grayish brown to dark grayish brown (values of 4 to 5) when dry and very dark brown, very dark grayish brown, to very dark gray (values of 2 to 3) when moist. Structure typically is medium to fine granular or subangular blocky parting to granular. -
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
Combination of shallow and deep rooted species (mid and tall rhizomatous and tufted perennial cool season grasses) with fine and coarse roots positively influences infiltration. Invasion of introduced cool-season grasses such as Kentucky bluegrass and crested wheatgrass may have an adverse impact infiltration and runoff.
Relative composition is approximately 75 percent grasses, 10 percent grass-like plants, 10 percent forbs, and 5 percent shrubs. The grass component is composed of C3, rhizomatous, mid grasses (20-30%), C3, bunch, mid & short grasses (15-25%), C4, short grasses (5-15%), C4, mid and tall grasses (0-10%), grass-likes (5-10%). -
Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on this site):
None. When dry, B horizons can be hard and appear to be compacted, but no platy structure will be present. -
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:
Phase 1.1
1. Native, perennial, C3, rhizomatous grass, 360-540 #/ac, 20-30% (1 species minimum): western wheatgrass, thickspike wheatgrass.
2. Native, perennial, C3, bunchgrass, 270-450 #/ac, 15-25% (2 species minimum): green needlegrass, needle and thread, prairie Junegrass.
Phase 1.2
1. Native, perennial, C4, shortgrass, 240-480 #/ac, 20-40% (2 species minimum): blue grama, buffalograss.Sub-dominant:
Phase 1.1
1. Native, perennial, C4, shortgrass, 90-270 #/ac, 5-15% (1 species minimum): blue grama, buffalograss.
Phase 1.2
1. Native, perennial, C3, rhizomatous, grass, 60-240 #/ac, 5-20% (1 species minimum): western wheatgrass, thickspike wheatgrass.
2. Native forbs, 60-180#/ac, 5-15% (5 species minimum): Species present will vary from location to location.Other:
Minor - Phase 1.1
1. Grass-likes, 90-180 #/ac, 5-10%: threadleaf sedge, other sedges.
2. Native forbs, 90-180 #/ac, 5-10%: Species will vary from location to location.
3. Native, perennial, C4, tall-and midgrass, 0-180#/ac, 0-10%: big bluestem, little bluestem, sideoats grama.
4. Shrubs: 0-180 #/ac, 0-10%: shrubs present will vary from location to location.
Minor - Phase 1.2
1. Grass-likes, 60-120 #/ac, 5-10%: threadleaf sedge.
2. Native, perennial, C3, bunchgrass, 24-120 #/ac, 2-10%: needle and thread, green needlegrass, prairie Junegrass, Sandberg bluegrass.
3. Native, perennial, C4, tall- and midgrass, 0-120 #/ac, 0-10%: sand dropseed, sideoats grama, plains muhly, little bluestem, threeawn.
4. Shrubs, 0-120 #/ac, 0-10%: Species present will vary from location to location.
5. Non-native, C3 grass, 0-60 #/ac, 0-5%: smooth brome, Kentucky bluegrass, cheatgrass.
Trace - Phase 1.2
1. Native, annual grass, 0-12 #/ac, 0-1%: Six weeks fescue.Additional:
The Rhizomatous Wheatgrass-Needle and Thread-Blue Grama Community or Reference Community (1.1) consists of seven F/S groups. These groups are native, perennial, C3, rhizomatous grass; native, perennial, C3 bunchgrass; grass-likes = native forbs; native, perennial, C4, tall- and midgrass = shrubs.
The Blue Grama-Rhizomatous Wheatgrass/Threadleaf sedge Community (1.2) includes seven F/S groups. These groups are native, perennial, C4, shortgrass; native, perennial, C3, rhizomatous grass; native forbs; grass-likes; native, perennial, C3, bunchgrass; native, perennial, C4 tall- and midgrass = shrubs; non-native, C3 grass; and native, annual grass. -
Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
Bunch grasses have strong, healthy centers with few (less than 3 percent) dead centers. Shrubs may show some dead branches (less than 5 percent) as plants age. -
Average percent litter cover (%) and depth ( in):
Plant litter cover is evenly distributed throughout the site and is expected to be 60 to 70 percent and at a depth of 0.25 to 0.50 inches (0.65 to 1.30 cm). Kentucky bluegrass excessive litter can negatively impact the functionality of this site. -
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
The representative value (RV) for annual production is 1,800 pounds per acre on an air dry weight basis. Low and High production years should yield 1,000 and 2,500 pounds per acre respectively. -
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:
No non-native invasive species are present. Annual bromes, Kentucky bluegrass, smooth brome, crested wheatgrass, and sweet clover are known invasives that have the potential to become dominant or co-dominant on this site. Consult the state noxious weed and state watch lists for potential invasive species. Note: species that become dominant for only one to several years (e.g., short-term response to drought or wildfire) are not invasive plants. -
Perennial plant reproductive capability:
All perennial species exhibit high vigor relative to recent weather conditions. Perennial grasses should have vigorous rhizomes or tillers; vegetative and reproductive structures are not stunted. All perennial species should be capable of reproducing annually.
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