Natural Resources
Conservation Service
Ecological site R058BY144WY
Saline Upland (SU) 10-17” PZ
Last updated: 9/15/2024
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.
MLRA notes
Major Land Resource Area (MLRA): 058B–Northern Rolling High Plains, Southern Part
MLRA 58B is located in northeastern Wyoming (95 percent) and extreme southeastern Montana (5 percent). It is comprised of sedimentary plains, scoria hills, and river valleys. The major rivers include the Powder, Tongue, Belle Fourche, Cheyenne, and North Platte. Tributaries include the Little Powder River, Little Missouri River, Clear Creek, Crazy Woman Creek, and others. This MLRA is traversed by Interstates 25 and 90, and U.S. Highways 14 and 16. The extent of MLRA 58B covers approximately 12.3 million acres. Major land uses include rangeland (approximately 93 percent), cropland, pasture, and hayland (approximately 2 percent), and forest, urban, and miscellaneous uses (approximately 5 percent). Cities include Buffalo, Casper, Sheridan, and Gillette, WY. Land ownership is mostly private. Federal lands include the Thunder Basin National Grassland (U.S. Forest Service) and lands administered by the Bureau of Land Management. Areas of interest in MLRA 58B in Wyoming include Fort Phil Kearny State Historic Site, Glendo State Park, and Lake DeSmet. The elevations in MLRA 58B increase gradually from north to south and range from approximately 2,900 to 5,900 feet. A few buttes are higher than 6,800 feet. The average annual precipitation in this area ranges from 10 to 17 inches per year. Precipitation occurs mostly during the growing season, often during rapidly developing thunderstorms. Mean annual air temperature is 46 degrees Fahrenheit. Summer temperatures may exceed 100 degrees Fahrenheit. Winter temperatures may drop to below zero. Snowfall averages 45 inches per year, but varies from 25 to over 70 inches in some locales.
Classification relationships
USDA Natural Resources Conservation Service (NRCS):
Land Resource Region─G Western Great Plains Range and Irrigation; Major Land Resource Area (MLRA)─58B Northern Rolling High Plains, Southern Part (USDA, 2006)
Relationship to Other Classifications:
USDA Forest Service (FS) Classification Hierarchy:
Province─331 Great Plains-Palouse Dry Steppe; Section─331G-Powder River Basin; Subsections─331Gb Montana Shale Plains, 331Ge Powder River Basin, 331Gf South Powder River Basin-Scoria Hills (Cleland et al, 1997)
Environmental Protection Agency (EPA) Classification Hierarchy:
Level III Ecoregion─43 Northwestern Great Plains; Level IV Ecoregion─43p Scoria Hills, 43q Mesic-Dissected Plains, 43w Powder River Basin (EPA, 2013)
https://www.epa.gov/eco-research/ecoregions
Ecological site concept
The Saline Upland 10-17” PZ ecological site occurs on nearly level to moderate slopes on sedimentary plains or uplands. It is a cool- and warm-season, mixed-grass prairie (mid- and shortgrasses), with secondary shrubs, and a minor component of forbs. The salts, sodium and carbonates in the soil is the major limiting or identifying factor.
Associated sites
| R058BY162WY |
Shallow Loamy (SwLy) 10-14” PZ Shallow Loamy will tend to be on steep slopes above or below the Saline Upland. |
|---|---|
| R058BY158WY |
Shallow Clayey (SwCy) 10-14” PZ Shallow Clayey will tend to be on steep slopes above or below the Saline Upland. |
Similar sites
| R058BY138WY |
Saline Lowland (SL) 10-14” PZ Saline Lowland 10-14 has a water influence from runoff and spring flood events, saline upland is a dry upland site. |
|---|
Table 1. Dominant plant species
| Tree |
Not specified |
|---|---|
| Shrub |
(1) Atriplex gardneri |
| Herbaceous |
(1) Pascopyrum smithii |
Physiographic features
This site occurs on nearly level to moderately sloping alluvial fans, fan remnants, hills, and stream terraces; on sedimentary plains or uplands.
Table 2. Representative physiographic features
| Landforms |
(1)
Alluvial fan
(2) Fan remnant (3) Hill (4) Stream terrace |
|---|---|
| Runoff class | Medium to very high |
| Flooding frequency | None |
| Ponding frequency | None |
| Elevation | 1,036 – 1,829 m |
| Slope | 0 – 15% |
| Aspect | Aspect is not a significant factor |
Climatic features
The average annual precipitation ranges from 10 to 17 inches per year across MLRA 58B. There are two precipitation zones (PZ). The 10 to 14 inch precipitation zone is predominant across the MLRA, including portions of Sheridan, Johnson, and Natrona Counties; portions of Campbell and Converse Counties; and smaller portions of Weston and Niobrara Counties. The 15 to 17 inch precipitation zone occurs in northern and eastern portions of the MLRA, including portions of Sheridan, Campbell, and western Crook Counties. Wide fluctuations in precipitation may occur from year to year, and occasional periods of extended drought (longer than one year in duration) can be expected. Two-thirds of the annual precipitation occurs during the growing season from May through September. Mean Annual Air Temperature (MAAT) is 46 degrees Fahrenheit. Cold air outbreaks from Canada in winter move rapidly from northwest to southeast and account for extreme minimum temperatures. Chinook winds may also occur in winter and bring rapid rises in temperature. Extreme storms may occur during the winter, but most severely affect ranching operations during late winter and spring. High-intensity afternoon thunderstorms may occur during the summer. Annual wind speeds average about 5 mph. Daytime winds are generally stronger than nighttime winds. Occasional strong storms may bring brief periods of high winds with gusts of more than 75 mph. The average length of the freeze-free period (28 degrees Fahrenheit) is 125 days and generally occurs from May 16 to September 19. The average frost-free period (32 degrees Fahrenheit) is 101 days and generally occurs from June 1 to September 9.
The growth of native cool-season plants begins in late April to early May with peak growth occurring in mid to late June. Native warm-season plants begin growth in late May to early June and continue into August. Regrowth of cool-season plants occurs in September in most years, depending upon moisture.
Note: The climate described here is based on historic climate station data and is averaged to provide an overview of the annual precipitation, temperatures, and growing season. Future climate is beyond the scope of this document. However, research to determine the effects of elevated CO2 and heating on mixed-grass prairie ecosystems, and how it may relate to future plant communities, is ongoing.
For detailed information, or to find a specific climate station, visit the Western Regional Climate Center (WRCC) website: Western Regional Climate Center, Historical Data, Western U.S. Climate summaries, NOAA Coop Stations, Wyoming (Note: Montana climate stations are also listed under the Wyoming link).
https://wrcc.dri.edu/summary/Climsmwy.html
Wind speed averages can be found at the WRCC home page, under the Specialty Climate tab: https://wrcc.dri.edu/
The following tables represent area-wide climate data for the 10 to 17 inch precipitation zone:
Table 3. Representative climatic features
| Frost-free period (characteristic range) | 85-103 days |
|---|---|
| Freeze-free period (characteristic range) | 118-126 days |
| Precipitation total (characteristic range) | 330-381 mm |
| Frost-free period (actual range) | 82-104 days |
| Freeze-free period (actual range) | 116-127 days |
| Precipitation total (actual range) | 254-432 mm |
| Frost-free period (average) | 101 days |
| Freeze-free period (average) | 125 days |
| Precipitation total (average) | 356 mm |
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
Climate stations used
-
(1) CASPER NATRONA CO AP [USW00024089], Casper, WY
-
(2) WRIGHT 12W [USC00489805], Gillette, WY
-
(3) DULL CTR 1SE [USC00482725], Douglas, WY
-
(4) MIDWEST [USC00486195], Midwest, WY
-
(5) WESTON 1 E [USC00489580], Weston, WY
-
(6) GILLETTE 4SE [USC00483855], Gillette, WY
-
(7) DILLINGER [USC00482580], Gillette, WY
Influencing water features
This upland ecological site is not influenced by a water table or run in from adjacent sites. Due to the semi-arid climate in which it occurs, the water budget is normally contained within the soil pedon. Soil moisture is recharged by spring rains, but it rarely exceeds field capacity in the upper 40 inches before being depleted by evapotranspiration. During intense precipitation events, precipitation rates frequently exceed infiltration rates and the site delivers moisture to downslope sites through surface runoff. Moisture loss through evapotranspiration exceeds precipitation for a majority of the growing season. Soil moisture is the primary limiting factor for vegetative production on this ecological site.
Soil features
The soils on this site are typically deep to very deep but include moderately deep, well drained soils that formed from alluvium; moderately deep soils formed from residuum derived from sandstone, shale, and siltstone. They typically have a very slow to slow permeability class, but range to moderately slow or impermeable in some soils. The available water capacity is typically moderate, but may range to low or high in some soils. The surface layer of the soils in this site are typically loam or silty clay loam, but may include clay loam, fine sandy loam, or very fine sandy loam. The surface layer ranges from a depth of 1 to 8 inches thick. The subsoil is typically clay, clay loam or silty clay loam, but may also include loam, sandy clay loam, or silty clay. Rock fragments are typically 0 to 5 percent in the subsoil but may range up to 15 percent in some soils. Soils in this site are typically calcareous to the surface, but some pedons may be leached as deep as 5 to 32 inches. These soils are susceptible to the hazard of erosion by water and wind. The potential for water erosion accelerates with increasing slope. The soil moisture regime is typically ustic aridic. The soil temperature regime is mesic.
Major soil series correlated to this ecological site include: Absted, Arvada, Cedar Butte, and Keyner.
The attributes listed below represent 0-40 inches in depth or to the first restrictive layer.
Table 4. Representative soil features
| Parent material |
(1)
Alluvium
(2) Residuum |
|---|---|
| Surface texture |
(1) Loam (2) Silty clay loam (3) Clay loam (4) Fine sandy loam (5) Very fine sandy loam (6) Silt loam |
| Drainage class | Well drained |
| Permeability class | Very slow to slow |
| Depth to restrictive layer | 102 – 203 cm |
| Soil depth | 51 – 152 cm |
| Surface fragment cover <=3" | 0 – 5% |
| Available water capacity (Depth not specified) |
9.14 – 21.34 cm |
| Calcium carbonate equivalent (Depth not specified) |
0 – 10% |
| Electrical conductivity (Depth not specified) |
4 – 16 mmhos/cm |
| Sodium adsorption ratio (Depth not specified) |
5 – 25 |
| Soil reaction (1:1 water) (Depth not specified) |
6.1 – 9 |
| Subsurface fragment volume <=3" (Depth not specified) |
0 – 15% |
Table 5. Representative soil features (actual values)
| Drainage class | Not specified |
|---|---|
| Permeability class | Moderately slow |
| Depth to restrictive layer | 51 – 203 cm |
| Soil depth | Not specified |
| Surface fragment cover <=3" | Not specified |
| Available water capacity (Depth not specified) |
Not specified |
| Calcium carbonate equivalent (Depth not specified) |
Not specified |
| Electrical conductivity (Depth not specified) |
Not specified |
| Sodium adsorption ratio (Depth not specified) |
Not specified |
| Soil reaction (1:1 water) (Depth not specified) |
Not specified |
| Subsurface fragment volume <=3" (Depth not specified) |
Not specified |
Ecological dynamics
The Reference state is the plant community in which interpretations are primarily based and is used as a reference in order to understand the original potential of the site. The Reference state evolved under the combined influences of climatic conditions, periodic fire activity, grazing by large herbivores, and impacts from small mammals and insects. Changes may occur to the Reference State due to management actions such as continuous season-long or year-long grazing, increased stocking rates, climatic conditions such as drought, and natural events. The Reference State is characterized by cool-season rhizomatous midgrasses (western- and thickspike wheatgrass), warm-season bunch midgrass (alkali sacaton), cool-season mid bunchgrasses (Indian ricegrass, Sandberg bluegrass), and warm-season shortgrass (blue grama). Shrubs such as Gardner’s saltbush, fourwing saltbush, and winterfat, are also present. The Reference state is not necessarily the management goal, as other vegetative states may be considered desired plant communities as long as critical resource concerns are met.
In addition to the Reference state, other plant communities can occur on this site and are usually the result of historic management practices. Grazing practices such as continuous season-long or year-long grazing, heavier stocking rates, or a combination of these factors on this ecological site results in bunchgrasses such as alkali sacaton and rhizomatous wheatgrasses decreasing in both frequency and production. Grasses such as inland saltgrass will increase. Gardner’s saltbush and winterfat will also be reduced. Forbs and shrubs such as curlycup gumweed, woodyaster, broom snakeweed, and greasewood will also increase. Over the long-term, this continuous use in combination with high stock densities, will result in bare ground developing, and species such as field brome (also known as Japanese brome), and cheatgrass invading. There are various transitional stages which may occur on this ecological site. The information presented is representative of a dynamic set of plant communities that illustrate the complex interaction of several ecological processes.
State and transition model
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Ecosystem states
| T1A | - | Long-term excessive grazing or frequent and severe defoliation without adequate recovery between grazing events, or heavy, excessive grazing with overstocking |
|---|
State 1 submodel, plant communities
| 1.1A | - | Excessive grazing without adequate recovery between grazing events, and extended drought |
|---|---|---|
| 1.2A | - | Grazing that allows for adequate recovery between grazing events, along with proper stocking rates |
State 2 submodel, plant communities
State 1
Reference
The Reference state is characterized by two distinct plant communities.. The plant communities, and successional stages between them, represent the natural range of variability within the Reference state.
Dominant plant species
-
Gardner's saltbush (Atriplex gardneri), shrub
-
alkali sacaton (Sporobolus airoides), grass
-
western wheatgrass (Pascopyrum smithii), grass
-
saltgrass (Distichlis spicata), grass
Community 1.1
Gardner’s Saltbush, Alkali Sacaton, and Western Wheatgrass
This is the interpretive plant community for the Saline Upland 10 to 17 inch Precipitation Zone ecological site. It is well adapted to the Northern Great Plains climate. This community developed with grazing by large herbivores and is suited to grazing by domestic livestock. Historically, fires likely occurred infrequently, and were randomly distributed. This plant community can be found on areas where grazed plants receive adequate periods of recovery during the growing season. The potential vegetation is about 50 to 60 percent grasses and grass-likes, 5 percent forbs, and 40 to 45 percent woody plants. The major grasses include western wheatgrass, thickspike wheatgrass, alkali sacaton, Indian ricegrass, Sandberg bluegrass, and blue grama. Secondary and minor grasses include prairie Junegrass, bottlebrush squirreltail, and inland saltgrass. Forbs include scarlet globemallow, textile onion, and rush skeletonplant. Other forbs include white- and purple prairie clover, prairie coneflower, and American vetch. Shrubs such Gardner’s saltbush, fourwing saltbush, winterfat, rubber rabbitbrush, and big sagebrush; broom snakeweed, plains pricklypear and black greasewood also occur. See the species composition list. Plant diversity is high. In the Saline Upland 10 to 17 inch Precipitation Zone ecological site, the total annual production (air-dry weight) is about 600 pounds per acre during an average year, but it can range from about 350 pounds per acre in unfavorable years to about 750 pounds per acre in above-average years. Defoliation levels should be determined as part of a grazing management plan based on objectives. Community dynamics (nutrient and water cycles, and energy flow) are functioning properly. Infiltration rates are moderate, and soil erosion is low. Litter is properly distributed where vegetative cover is continuous. Plant decadence and natural mortality is low. This community is resistant to many disturbances except excessive grazing and development into urban or other uses.
Figure 6. Annual production by plant type (representative values) or group (midpoint values)
Table 6. Annual production by plant type
| Plant type | Low (kg/hectare) |
Representative value (kg/hectare) |
High (kg/hectare) |
|---|---|---|---|
| Grass/Grasslike | 211 | 456 | 701 |
| Shrub/Vine | 252 | 463 | 673 |
| Forb | 15 | 30 | 45 |
| Total | 478 | 949 | 1419 |
Figure 7. Plant community growth curve (percent production by month). WY1401, 10-14NP 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 | 30 | 35 | 10 | 5 | 5 | 5 | 0 | 0 |
Community 1.2
Gardner’s Saltbush, Alkali Sacaton, and Inland Saltgrass
This plant community developed with seasonal-use grazing, or excessive grazing without adequate recovery opportunity during the growing season. Green needlegrass may initially increase or decrease depending on the season of grazing use. Palatable forbs and shrubs such as white- and purple prairie clover and winterfat are present in reduced amounts. Hairy false goldenaster, large Indian breadroot, and scarlet globemallow have increased. Eventually, long-term excessive grazing, or frequent and severe defoliation without adequate recovery during the growing season, grazing-tolerant species such as inland saltgrass, blue grama and/or buffalograss, and threadleaf sedge will continue to increase. Eventually Rhizomatous wheatgrasses are reduced or nearly absent. Forbs such as scarlet globemallow and curlycup gumweed, and rush skeletonplant have increased. Palatable shrubs such as Gardner’s saltbush, fourwing saltbush and winterfat have been reduced, and shrubs such as broom snakeweed, pricklypear, and black greasewood, have increased. Natural disturbances such as drought can contribute to this shift. In the Saline Upland 10 to 17 inch Precipitation Zone, the total annual production (air-dry weight) is about 400 pounds per acre during an average year, but it can range from about 150 pounds per acre in unfavorable years to about 550 pounds per acre in above average years. This plant community is at risk of crossing an ecological threshold to the Eroded state. Total aboveground biomass has been reduced. Reduction of rhizomatous wheatgrasses, nitrogen-fixing forbs, and increased warm-season shortgrasses have begun to alter the biotic integrity of this community. Water and nutrient cycles may be impaired. Nearly all plant species typically found in community 1.1 are present and will respond to changes in grazing management.
Figure 8. Plant community growth curve (percent production by month). WY5803, Northern Rolling High Plains, Southern Part, 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 |
| 3 | 10 | 20 | 28 | 21 | 10 | 5 | 3 |
Pathway 1.1A
Community 1.1 to 1.2
Excessive grazing without adequate recovery between grazing events, and extended drought can shift this plant community toward community 1.2. Over a period of years, plant species less tolerant to frequent and severe defoliation will decrease, and those more tolerant will increase. Excessive grazing from year-to-year will result in a reduction or loss of cool-season species. Biotic integrity and water and nutrient cycles may become impaired because of this community pathway.
Pathway 1.2A
Community 1.2 to 1.1
Grazing that allows for adequate recovery between grazing events, along with proper stocking rates, will shift community 1.2 back toward community 1.1. Natural disturbances such as return to normal precipitation patterns will contribute to this shift.
State 2
Eroded
The Eroded state develops with long-term excessive grazing or frequent and severe defoliation, without adequate recovery between grazing events, or heavy, excessive grazing with overstocking, will cause a shift across an ecological threshold to the Increased Bare Ground state. An ecological threshold has been crossed. Erosion and loss of organic matter or carbon reserves are resource concerns.
Dominant plant species
-
greasewood (Sarcobatus vermiculatus), shrub
-
plains pricklypear (Opuntia polyacantha), shrub
-
saltgrass (Distichlis spicata), grass
-
Fendler's threeawn (Aristida purpurea var. fendleriana), grass
Community 2.1
Greasewood, Pains Pricklypear, Inland Saltgrass, and Fendler’s Threeawn
This plant community occurs where the rangeland is grazed year-round, at high stock densities. Physical impact such as trampling, soil compaction, and trailing typically contribute to this transition. The plant composition is made of annuals with a few species of perennial forbs and grasses that are very tolerant to frequent and severe defoliation. The dominant grasses include Fendler’s threeawn and inland saltgrass. Threadleaf sedge may persist. Plants such as Russian thistle, kochia, and other annuals are prevalent. Annual bromes such as field brome (also known as Japanese brome), and cheatgrass invade. Woodyaster, broom snakeweed, pricklypear, and black greasewood will persist. In the Saline Upland 10 to 17 inch Precipitation Zone ecological site, the total annual production (air-dry weight) is about 300 pounds per acre during an average year, but it can range from about 150 pounds per acre in unfavorable years to about 450 pounds per acre in above average years. Soil erosion hazard has increased due to the increase of bare ground. Runoff is typically high and infiltration is low. All ecological functions are impaired. Desertification is advanced.
Figure 9. Plant community growth curve (percent production by month). WY5804, Northern Rolling High Plains, Southern Part upland w/warm-season. 10-14" PZ, with warm-season dominant grasses and forbs.
| 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 | 20 | 35 | 30 | 8 | 2 |
Transition T1A
State 1 to 2
Long-term excessive grazing or frequent and severe defoliation without adequate recovery between grazing events, or heavy, excessive grazing with overstocking, will cause a shift across an ecological threshold to the Eroded state.
Additional community tables
Table 7. Community 1.1 plant community composition
| Group | Common name | Symbol | Scientific name | Annual production (kg/hectare) | Foliar cover (%) | |
|---|---|---|---|---|---|---|
|
Grass/Grasslike
|
||||||
| 1 | Cool-Season Rhizomatous | 28–135 | ||||
| western wheatgrass | PASM | Pascopyrum smithii | 28–135 | 1–15 | ||
| thickspike wheatgrass | ELLAL | Elymus lanceolatus ssp. lanceolatus | 28–135 | 1–15 | ||
| 2 | Cool-Season Bunch Midgrass | 112–342 | ||||
| Indian ricegrass | ACHY | Achnatherum hymenoides | 28–90 | 5–10 | ||
| squirreltail | ELEL5 | Elymus elymoides | 28–90 | 5–10 | ||
| Grass, perennial | 2GP | Grass, perennial | 28–90 | 5–10 | ||
| Sandberg bluegrass | POSE | Poa secunda | 28–73 | 5–10 | ||
| 3 | Warm-Season Bunchgrass | 71–224 | ||||
| saltgrass | DISP | Distichlis spicata | 43–135 | 5–15 | ||
| alkali sacaton | SPAI | Sporobolus airoides | 28–90 | 5–10 | ||
|
Forb
|
||||||
| 5 | Forb | 15–45 | ||||
| Forb, perennial | 2FP | Forb, perennial | 15–45 | 1–5 | ||
| aster | ASTER | Aster | 15–45 | 1–5 | ||
| desertparsley | LOMAT | Lomatium | 15–45 | 1–5 | ||
| milkvetch | ASTRA | Astragalus | 15–45 | 1–5 | ||
| purple prairie clover | DAPU5 | Dalea purpurea | 15–45 | 1–5 | ||
| white prairie clover | DACA7 | Dalea candida | 15–45 | 1–5 | ||
| textile onion | ALTE | Allium textile | 15–45 | 1–5 | ||
| tapertip hawksbeard | CRAC2 | Crepis acuminata | 15–45 | 1–5 | ||
| American vetch | VIAM | Vicia americana | 15–45 | 1–5 | ||
| smooth woodyaster | XYGL | Xylorhiza glabriuscula | 15–45 | 1–5 | ||
| scarlet beeblossom | GACO5 | Gaura coccinea | 15–45 | 1–5 | ||
|
Shrub/Vine
|
||||||
| 6 | Subshrubs/Shrubs | 252–673 | ||||
| Gardner's saltbush | ATGA | Atriplex gardneri | 140–364 | 10–50 | ||
| greasewood | SAVE4 | Sarcobatus vermiculatus | 28–90 | 5–10 | ||
| Shrub (>.5m) | 2SHRUB | Shrub (>.5m) | 28–73 | 5–10 | ||
| winterfat | KRLA2 | Krascheninnikovia lanata | 28–73 | 5–10 | ||
| Subshrub (<.5m) | 2SUBS | Subshrub (<.5m) | 28–73 | 5–10 | ||
Interpretations
Animal community
Animal Community – Wildlife Interpretations (from 2001 ESD, will be revised in future updates)
Gardners Saltbrush/ winterfat (Reference): The predominance of woody plants in this plant community provides winter grazing for mixed-feeders, such as bison, elk, and antelope. Suitable thermal and escape cover for deer may be limited due to the low quantities of tall woody plants. When found adjacent to sagebrush dominated states, this plant community may provide lek sites for sage grouse. Other birds that would frequent this plant community include western meadowlarks, horned larks, and golden eagles. Some grassland obligate small mammals would occur here.
Greasewood/woody aster: This plant community exhibits a low level of plant species diversity due to the accumulation of salts in the soil. It may provide some thermal and escape cover for deer and antelope if no other woody community is nearby, but in most cases it is not a desirable plant community to select as a wildlife habitat management objective.
Animal Community – Grazing Interpretations (updated in 2019 Provisional revision)
The following table is a guide to stocking rates for the plant communities described in the Saline Upland 10 to 17 inch Precipitation Zone ecological site. These are conservative estimates for initial planning. On-site conditions will vary, and stocking rates should be adjusted based on range inventories, animal kind/class, forage availability (adjusted for slope and distance to water), and the type of grazing system (number of pastures, planned moves, etc.), all of which is determined in the conservation planning process.
The following stocking rates are based on the total annual forage production in a normal year multiplied by 25 percent harvest efficiency of preferred and desirable forage species, divided by 912 pounds of ingested air-dry vegetation for an animal unit per month (Natl. Range and Pasture Handbook, 1997). An animal unit month is defined as the amount of forage required by one livestock animal, with or without one calf, for one month, and is shortened to AUM.
Plant Community (PC) Production (total lbs./acre in a normal year) and Stocking Rate (AUM/acre) are listed below:
Example:
600 lbs. per acre X 25% Harvest Efficiency = 150 lbs. forage demand for one month. 150 lbs. per acre/912 demand per AUM =0.16
Reference Plant Community 250-650 .15
Greasewood/woody aster 250-400 .05
Increased Bare Ground PC (*) (*)
* Highly variable stocking rates need to be determined on site.
Grazing by domestic livestock is one of the major income-producing industries in the area. Rangelands in this area provide year-long forage under prescribed grazing for cattle, sheep, horses and other herbivores. During the dormant period, livestock may need supplementation based on reliable forage analysis.
Hydrological functions
Water and salinity are the principal factors limiting forage production on this site. This site is dominated by soils in hydrologic group B and C, with localized areas in hydrologic group D. Infiltration ranges from slow to moderate. Runoff potential for this site varies from moderate to high depending on soil hydrologic group 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 short-grasses form a strong sod and dominate the site. Areas where ground cover is less than 50 percent have the greatest potential to have reduced infiltration and higher runoff (refer to Part 630, NRCS National Engineering Handbook for detailed hydrology information).
Rills are common on this site. They are typically connected and may begin to form deep rills. Some gullies may appear in concentrated flow areas on steep slopes (greater than 15 percent), or on lower slopes where runoff exits the slope. Water flow patterns are normally broken and irregular, becoming continuous on steeper slopes (greater than 15 percent). Debris dams will be evident and/or common.. Pedestals are noticeable and common but with few exposed roots. Pedestalled plants may include bunchgrasses and/or shrubs. Litter typically falls in place, and signs of movement are not common. Chemical and physical crusts may be present. Cryptogamic crusts are present, but only cover 1 to 2 percent of the soil surface.
Recreational uses
This site provides some hunting opportunities for upland game species.
Wood products
No appreciable wood products are present on the site.
Other products
None noted.
Other information
Site Development & Testing Plan
General Data (MLRA and Revision Notes, Hierarchical Classification, Ecological Site Concept, Physiographic, Climate, and Water Features, and Soils Data):
Updated. All “Required” items complete to Provisional level
Community Phase Data (Ecological Dynamics, STM, Transition & Recovery Pathways, Reference Plant Community, Species Composition List, Annual Production Table):
Updated. All “Required” items complete to Provisional level.
Annual Production Table is from the “Previously Approved” ESD (2001).
The Annual Production Table and Species Composition List will be reviewed for future updates at the Approved level.
Each Alternative State/Community
Complete to Provisional level
Supporting Information (Site Interpretations, Assoc. & Similar Sites, Inventory Data References, Agency/State Correlation, References)
Updated. All “Required” items complete to Provisional level.
Wildlife Interpretations: Narrative is from “Previously Approved” ESD (2001). Wildlife species will need to be updated at the next Approved level.
Livestock Interpretations: Plant community names and stocking rates updated.
Hydrology, Recreational Uses, Wood Products, and Other Products carried over from previously “Approved” ESD (2001).
Existing NRI Inventory Data References updated. More field data collection is needed to support this site concept.
Reference Sheet
Rangeland Health Reference Sheet carried over from previously “Approved” ESD (2005).
It will be updated at the next “Approved” level.
“Future work, as described in a project plan, to validate the information in this provisional ecological site description is needed. This will include field activities to collect low and medium intensity sampling, soil correlations, and analysis of that data. Annual field reviews should be done by soil scientists and vegetation specialists. A final field review, peer review, quality control, and quality assurance reviews of the ESD will be needed to produce the final document.” (NI 430_306 ESI and ESD, April 2015)
Supporting information
Inventory data references
Inventory data has been collected on private and federal lands by the following methods:
• Double Sampling (Determining Vegetation Production and Stocking Rates, WY-ECS-1)
• Rangeland Health (Interpreting Indicators of Rangeland Health, Version 4, 2005)
• Soil Stability (Interpreting Indicators of Rangeland Health, Version 4, 2005)
• Line Point Intercept (Monitoring Manual for Grassland, Shrubland, and Savanna Ecosystems, Volume II, 2005)
• Soil Pedon Descriptions (Field Book for Describing and Sampling Soils, Version 3, 2012)
• SCS-RANGE-417 (Production & Composition Record for Native Grazing Lands)
National Resources Inventory (NRI)
Number of Records: 19
Sample Period: 2004-2016
Counties: Campbell, Crook, Natrona, Weston
Additional data collection includes ESI data collection in conjunction with Soil Surveys conducted within MLRA 58B; ocular estimates; rangeland vegetative clipping for NRCS program support; field observations from experienced rangeland personnel
Data collection for this ecological site was done in conjunction with the progressive soil surveys within MLRA 58B Northern Rolling High Plains (Southern Part)
Note: Revisions to soil surveys are on-going. For the most recent updates, visit the Web Soil Survey, the official site for soils information: http://websoilsurvey.nrcs.usda.gov/app/WebSoilSurvey.aspx
Other references
Anderson, R.C. 2006. Evolution and origin of the central grassland of North America: Climate, fire, and mammalian grazers. Journal of the Torrey Botanical Society 133:626–647.
Bragg, T.B. 1995. The physical environment of the Great Plains grasslands. In: A. Joern and K.H. Keeler (eds) The changing prairie. Oxford University Press, Oxford, UK, pages 49–81.
Branson, D.H. and G.A. Sword. 2010. An experimental analysis of grasshopper community responses to fire and livestock grazing in a northern mixed-grass prairie. Environmental Entomology 39:1441–1446.
Brinson, M.M. 1993. A hydrogeomorphic classification for wetlands. Technical Report WRP–DE–4. U.S. Army Corps of Engineers Waterways Experiment Station, Vicksburg, MS.
Cleland, D., P. Avers, W.H. McNab, M. Jensen, R. Bailey, T. King, and W. Russell. 1997. National hierarchical framework of ecological units. In: Ecosystem Management: Applications for Sustainable Forest and Wildlife Resources, Yale University Press.
Coupland, R.T. 1958. The effects of fluctuations in weather upon the grasslands of the Great Plains. Botanical Review 24:273–317.
Davis, S.K., R.J. Fisher, S.L. Skinner, T.L. Shaffer, and R.M. Brigham. 2013. Songbird abundance in native and planted grassland varies with type and amount of grassland in the surrounding landscape. Journal of Wildlife Management 77:908–919.
DeLuca, T.H. and P. Lesica. 1996. Long-term harmful effects of crested wheatgrass on Great Plains grassland ecosystems. Journal of Soil and Water Conservation 51:408–409.
Derner, J.D. and R.H. Hart. 2007. Grazing-induced modifications to peak standing crop in northern mixed-grass prairie. Rangeland Ecology and Management 60:270–276.
Derner, J.D., and A.J. Whitman. 2009. Plant interspaces resulting from contrasting grazing management in northern mixed-grass prairie: Implications for ecosystem function. Rangeland Ecology and Management 62:83–88.
Derner, J.D., W.K. Lauenroth, P. Stapp, and D.J. Augustine. 2009. Livestock as ecosystem engineers for grassland bird habitat in the western Great Plains of North America. Rangeland Ecology and Management 62:111–118.
Dillehay, T.D. 1974. Late Quaternary bison population changes on the southern Plains. Plains Anthropologist 19:180–196.
Dormaar, J.F. and S. Smoliak. 1985. Recovery of vegetative cover and soil organic matter during revegetation of abandoned farmland in a semiarid climate. Journal of Range Management 38:487–491.
Guyette, Richard P., M.C. Stambaugh, D.C. Dey, and R.M. Muzika. (2012). Predicting fire frequency with chemistry and climate. Ecosystems, 15: 322-335.
Harmoney, K.R. 2007. Grazing and burning Japanese brome (Bromus japonicus) on mixed grass rangelands. Rangeland Ecology and Management 60:479–486.
Heitschmidt, R.K. and L.T. Vermeire. 2005. An ecological and economic risk avoidance drought management decision support system. In: J.A. Milne (ed.) Pastoral systems in marginal environments, 20th International Grasslands Congress, July, 2005. Page 178.
Knopf, F.L. 1996. Prairie legacies—Birds. In: F.B. Samson and F.L. Knopf (eds.) Prairie conservation: Preserving North America’s most endangered ecosystem. Island Press, Washington, DC. Pages 135–148.
Knopf, F.L. and F.B. Samson. 1997. Conservation of grassland vertebrates. In: F.B. Samson and F.L. Knopf (eds.) Ecology and conservation of Great Plains vertebrates: Ecological Studies 125. Springer-Verlag, New York, NY. Pages 273–289.
Lauenroth, W.K., O.E. Sala, D.P. Coffin, and T.B. Kirchner. 1994. The importance of soil water in recruitment of Bouteloua gracilis in the shortgrass steppe. Ecological Applications 4:741–749.
Laycock, W.A. 1988. History of grassland plowing and grass planting on the Great Plains. In: J.E. Mitchell (ed.) Impacts of the Conservation Reserve Program in the Great Plains—symposium proceedings, September 16–18, 1987. U.S. Dept. of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station, General Technical Report RM-158.
Malloch, D.W., K.A. Pirozynski, and P.H. Raven. 1980. Ecological and evolutionary significance of mycorrhizal symbioses in vascular plants (a review). Proceedings of the National Academy of Sciences 77:2113–2118.
Ogle, S.M., W.A. Reiners, and K.G. Gerow. 2003. Impacts of exotic annual brome grasses (Bromus spp.) on ecosystem properties of the northern mixed grass prairie. American Midland Naturalist 149:46–58.
Roath, L.R. 1988. Implications of land conversions and management for the future. In: J.E. Mitchell (ed.) Impacts of the Conservation Reserve Program in the Great Plains—symposium proceedings, September 16–18, 1987. U.S. Dept. of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station, General Technical Report RM-158.
Smoliak, S. and J.F. Dormaar. 1985. Productivity of Russian wildrye and crested wheatgrass and their effect on prairie soils. Journal of Range Management 38:403–405.
Smoliak, S., J.F. Dormaar, and A. Johnston. 1972. Long-term grazing effects on Stipa-Bouteloua prairie soils. Journal of Range Management 25:246–250.
Soil Survey Division Staff. 2017. Soil survey manual. U.S. Dept. of Agriculture Handbook 18.
Soil Survey Staff. Official Soil Series Descriptions. U.S. Dept. of Agriculture, Natural Resources Conservation Service. Available online. https://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/home/?cid=nrcs142p2_053587. Accessed 15 November, 2017.
Soil Survey Staff. Soil Survey Geographic (SSURGO) database. U.S. Dept. of Agriculture, Natural Resources Conservation Service.
Soil Survey Staff. 2014. Keys to Soil Taxonomy, 12th edition. U.S. Dept. of Agriculture, Natural Resources Conservation Service.
Soil Survey Staff. 2018. Web Soil Survey. U.S. Dept. of Agriculture, Natural Resources Conservation Service. Available online. https://websoilsurvey.nrcs.usda.gov/app/. Accessed 15 February, 2018.
Soller, D.R. 2001. Map showing the thickness and character of Quaternary sediments in the glaciated United States east of the Rocky Mountains. U.S. Geological Survey Miscellaneous Investigations Series I-1970-E, scale 1:3,500,000.
Stewart, Omer C. 2002. Forgotten Fires. Univ. of Oklahoma Press, Norman, OK.
United States Department of Agriculture, Natural Resources Conservation Service. Glossary of landform and geologic terms. National Soil Survey Handbook, Title 430-VI, Part 629.02c. Available online. http://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/ref/?cid=nrcs142p2_054242.(Accessed 16 January, 2018.
United States Army Corps of Engineers. 1987. Corps of Engineers wetlands delineation manual. Wetlands Research Program Technical Report Y-87-1 (http://www.lrh.usace.army.mil/Portals/38/docs/USACE%2087%20Wetland%20Delineation%20Manual.pdf). Waterways Experiment Station, Vicksburg, MS.
United States Environmental Protection Agency, National Health and Environmental Effects Research Laboratory. 2013. Level III ecoregions of the continental United States. Available online. https://www.epa.gov/eco-research/ecoregions. Accessed 30 January, 2019.
United States Department of Agriculture, Natural Resources Conservation Service. 2010a. Field indicators of hydric soils in the United States, version 7.0.
United States Department of Agriculture, Natural Resources Conservation Service. 2013a. Climate data. National Water and Climate Center. Available online. http://www.wcc.nrcs.usda.gov/climate. Accessed 13 October, 2017.
United States 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.
United States Department of Agriculture, Natural Resources Conservation Service. 2013b. National Soil Information System. https://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/survey/geo/?Cid=nrcs142p2_053552 (Accessed 30 October, 2017).
United States Department of the Interior, Geological Survey. 2008. LANDFIRE 1.1.0 Vegetation Dynamics Models. http://landfire.cr.usgs.gov/viewer/.
United States Department of the Interior, Geological Survey. 2011. LANDFIRE 1.1.0 Existing Vegetation Types. http://landfire.cr.usgs.gov/viewer/.
Willeke, G.E. 1994. The national drought atlas [CD ROM]. U.S. Army Corps of Engineers, Water Resources Support Center, Institute for Water Resources Report 94-NDS-4.
Wilson, S.D. and J.M. Shay. 1990. Competition, fire, and nutrients in a mixed-grass prairie. Ecology 71:1959–1967.
With, K.A. 2010. McCown’s longspur (Rhynchophanes mccownii). In: A. Poole (ed.) The birds of North America [online]. Cornell Lab of Ornithology, Ithaca, NY. https://birdsna.org/Species-Account/bna/home.
Augustine, D.J., J. Derner, D. Milchunas, D. Blumenthal, and L. Porensky. 2017. Grazing moderates increases in C3 grass abundance over seven decades across a soil texture gradient in shortgrass steppe. In: Journal of Vegetation Science, DOI:10.1111/jvs.12508.
Clark, J., E. Grimm, J. Donovan, S. Fritz, D. Engrstom, and J. Almendinger. 2002. Drought cycles and landscape responses to past aridity on prairies of the Northern Great Plains, USA. Ecology, 83(3), Pages 595-601.
Connell, L. C., J. D. Scasta, and L. M. Porensky. 2018. Prairie dogs and wildfires shape vegetation structure in a sagebrush grassland more than does rest from ungulate grazing. Ecosphere 9(8):e02390. 10.1002/ecs2.2390.
Collins, S. and S. Barber. (1985). Effects of disturbance on diversity in mixed-grass prairie. In: Vegetatio, 64, pages 87-94.
Egan, Timothy. 2006. The Worst Hard Time. Houghton Mifflin Harcourt Publishing Company, New York, NY.
Guyette, R.P., M.C. Stambaugh, D.C. Dey, and R.M. Muzika. 2012. Predicting fire frequency with chemistry and climate. In: Ecosystems, 15: pages 322-335.
Hart, R., and J. Hart. 1997. Rangelands of the Great Plains before European settlement. In: Rangelands, 19(1), pages 4-11.
Hart, R. 2001. Plant biodiversity on shortgrass steppe after 55 years of zero, light, moderate, or heavy cattle grazing. In: Plant Ecology, 155, pages 111-118.
Pellant, M., P. Shaver, D.A. Pyke, and J.E. Herrick. 2005. Interpreting indicators of rangeland health, Version 4. United States Department of the Interior, Bureau of Land Management.
Porensky, L.M. and D.M. Blumenthal. 2016. Historical wildfires do not promote cheatgrass invasion in a western Great Plains steppe. In: Biological Invasions 18:3333-3349: DOI 10.1007/s10530-16-1225-z
Porensky, L., J.D. Derner, and D.W. Pellatz. 2018. Plant community responses to historical wildfire in a shrubland-grassland ecotone reveal hybrid disturbance response. In: Ecosphere. DOI: 9(8):e02363. 10.1002/ecs2.2363.
Mack, Richard N., and J.N. Thompson. 1982. Evolution in steppe with few large, hooved mammals. In: The American Naturalist. 119, No. 6, pages 757-773
Reyes-Fox, M., H. Stelzer, M.J. Trlica, G.S. McMaster, A.A. Andales, D.R. LeCain, and J.A. Morgan. 2014. Elevated CO2 further lengthens growing season under warming conditions. In: Nature, April 23, 2014. Available online. http://www.nature.com/nature/journal/v510/n7504/full/nature13207.html. Accessed 1 March, 2017.
Schoeneberger, P.J., D.A. Wysockie, E.C. Benham, and Soil Survey Staff. 2012. Field book for describing and sampling soils, Version 3.0. U.S. Dept. of Agriculture, Natural Resources Conservation Service.
Stahl, David W., E.R. Cook, M.K. Cleaveland, M.D. Therrell, D.M. Meko, H.D. Grissino-Mayer, E. Watson, and B.H. Luckman. Tree-ring data document 16th century megadrought over North America. 2000. In: Eos, 81(12), pages 121-125.
Stubbendieck, James, S.L. Hatch, and L.M. Landholt. 2003. North American wildland plants. Univ. of Nebraska Press, Lincoln and London.
Zelikova, T.J., D.M. Blumenthal, D.G. Williams, L. Souza, D.R. LeCain, and J. Morgan. 2014. Long-term exposure to elevated CO2 enhances plant community stability by suppressing dominant plant species in a mixed-grass prairie. In: Ecology, 2014 https://www.pnas.org/content/111/43/15456.
United States Department of Agriculture, Natural Resources Conservation Service. National Ecological Site Handbook, Title 190, Part 630, 1st Edition. Available online. https://directives.sc.egov.usda.gov/. Accessed 15 September, 2017.
United States Department of Agriculture, Natural Resources Conservation Service. 2009. Part 630, Hydrology, National Engineering Handbook
United States Department of Agriculture, Natural Resources Conservation Service. 1972-2012. National Engineering Handbook Hydrology Chapters. http://www.nrcs.usda.gov/wps/portal/nrcs/detailfull/national/water/?&cid=stelprdb1043063 (Accessed August, 2015).
United States Department of Agriculture, Natural Resources Conservation Service. 1997, revised 2003.
National Range and Pasture Handbook. http://www.glti.nrcs.usda.gov/technical/publications/nrph.html
(Accessed 26 February, 2018).
United States Department of Agriculture, Natural Resources Conservation Service. National Soil Survey Handbook title 430-VI. http://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/ref/?cid=nrcs142p2_054242
United States Department of Agriculture, Natural Resources Conservation Service. Web Soil Survey. Available online. http://websoilsurvey.sc.egov.usda.gov/App/WebSoilSurvey.aspx. Accessed 15 November, 2017.
United States Department of Commerce, National Oceanic and Atmospheric Administration (NOAA). Cooperative climatological data summaries. NOAA Western Regional Climate Center, Reno, NV. Available online. http://www.wrcc.dri.edu/climatedata/climsum.(Accessed 16 November, 2017.
Contributors
Everett Bainter
Glenn Mitchell
Approval
Kirt Walstad, 9/15/2024
Acknowledgments
Project Staff:
Kimberly Diller, Ecological Site Inventory Specialist, NRCS MLRA SSO, Pueblo CO
Mike Leno, Project Leader, NRCS MLRA SSO, Buffalo, WY
Partners/Contributors:
Joe Dyer, Soil Scientist, NRCS MLRA SSO, Buffalo, WY
Arnie Irwin, Soil Scientist, BLM, Buffalo, WY
Blaine Horn, Rangeland Extension Educator, UW Extension, Buffalo, WY
Isabelle Giuliani, Resource Soil Scientist, NRCS, Douglas, WY
Mary Jo Kimble, Project Leader, NRCS MLRA SSO, Miles City, MT
Ryan Murray, Rangeland Management Specialist, NRCS, Buffalo, WY
Lauren Porensky, Ph.D., Ecologist, ARS, Fort Collins, CO
Chadley Prosser, Rangeland Program Manager, USFS, Bismarck, ND
Bryan Christensen, Ecological Site Inventory Specialist, NRCS-MLRA SSO, Pinedale, WY
Marji Patz, Ecological Site Inventory Specialist, NRCS-MLRA SSO, Powell, WY
Rick Peterson, Ecological Site Inventory Specialist, NRCS-MLRA SSO, Rapid City, SD
Program Support:
John Hartung, WY State Rangeland Management Specialist-QC, NRCS, Casper, WY
David Kraft, NRCS MLRA Ecological Site Inventory Specialist-QA, Emporia, KS
Carla Green Adams, Editor, NRCS-SSR5, Denver, CO
Chad Remley, Regional Director, Northern Great Plains Soil Survey, Salina, KS
Those involved in developing the 2001 version: Everett Bainter, WY State Rangeland Management Specialist, WY-NRCS, and Glen Mitchell, Rangeland Management Specialist, WY-NRCS
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) | |
|---|---|
| Contact for lead author | |
| Date | 04/01/2005 |
| Approved by | Kirt Walstad |
| Approval date | |
| Composition (Indicators 10 and 12) based on | Annual Production |
Indicators
-
Number and extent of rills:
Rills should not be present. -
Presence of water flow patterns:
Barely observable. -
Number and height of erosional pedestals or terracettes:
Essentially non-existent. -
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
Bare ground is 30-40%. -
Number of gullies and erosion associated with gullies:
Active gullies should not be present. -
Extent of wind scoured, blowouts and/or depositional areas:
None -
Amount of litter movement (describe size and distance expected to travel):
Little to no plant litter movement. Plant litter
remains in place and is not moved by erosional forces. -
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
Plant cover and litter is at 50% or greater of soil surface and maintains soil surface
integrity. Soil Stability class is anticipated to be 4 or greater. -
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
Use Soil Series description for depth and color of A-horizon. -
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
Grass canopy and basal cover should reduce raindrop impact and slow overland flow providing increased time for infiltration to occur. Healthy deep rooted native grasses enhance infiltration and reduce runoff. Infiltration is slow to moderate. -
Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on this site):
No compaction layer or soil surface crusting should 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:
Shrubs >> Mid stature Grasses > Short stature Grasses ForbsSub-dominant:
Other:
Additional:
-
Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
Very Low -
Average percent litter cover (%) and depth ( in):
Average litter cover is 10-15% with depths of 0.1 to 0.5 inches. -
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
600 lbs./ac -
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:
Buffalograss, Inland saltgrass, Broom Snakeweed, and Species found on Noxious Weed List. -
Perennial plant reproductive capability:
All species are capable of reproducing.
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The Ecosystem Dynamics Interpretive Tool is an information system framework developed by the USDA-ARS Jornada Experimental Range, USDA Natural Resources Conservation Service, and New Mexico State University.
Click on box and path labels to scroll to the respective text.
Ecosystem states
| T1A | - | Long-term excessive grazing or frequent and severe defoliation without adequate recovery between grazing events, or heavy, excessive grazing with overstocking |
|---|
State 1 submodel, plant communities
| 1.1A | - | Excessive grazing without adequate recovery between grazing events, and extended drought |
|---|---|---|
| 1.2A | - | Grazing that allows for adequate recovery between grazing events, along with proper stocking rates |