Natural Resources
Conservation Service
Ecological site R058DY028SD
Shallow Sandy
Accessed: 04/26/2024
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.
Classification relationships
Level IV Ecoregions of the Conterminous United States: 43e – Sagebrush Steppe.
Associated sites
R058DY009SD |
Sandy |
---|---|
R058DY010SD |
Loamy |
R058DY026SD |
Thin Sandy |
Similar sites
R058DY010SD |
Loamy Loamy [more western wheatgrass; less needleandthread; more production] |
---|---|
R058DY009SD |
Sandy Sandy [more western wheatgrass; more production] |
Table 1. Dominant plant species
Tree |
Not specified |
---|---|
Shrub |
Not specified |
Herbaceous |
(1) Calamovilfa longifolia |
Physiographic features
This site occurs on moderate to steeply sloping uplands.
Table 2. Representative physiographic features
Landforms |
(1)
Ridge
|
---|---|
Flooding frequency | None |
Ponding frequency | None |
Elevation | 2,300 – 4,000 ft |
Slope | 6 – 40% |
Water table depth | 80 in |
Aspect | Aspect is not a significant factor |
Climatic features
The climate in this MLRA is typical of the drier portions of the Northern Great Plains where sagebrush steppes to the west yield to grassland to the east. Annual precipitation ranges from 14 to 16 inches. Most of the rainfall occurs as frontal storms early in the growing season. Some high intensity, convective thunderstorms occur in the summer. Precipitation in winter occurs as snow. Temperatures show a wide range between summer and winter and between daily maximums and minimums, due to the high elevation and dry air, which permits rapid incoming and outgoing radiation. Outbreaks of cold air from Canada in winter move rapidly from northwest to southeast and account for extreme minimum temperatures. Extreme storms may occur during the winter but most severely affect ranch operations during late winter and spring. The normal average annual temperature is about 44°F. January is the coldest month with average temperatures ranging from about 12°F (Marmarth, North Dakota (ND)), to about 20°F (Baker, Montana (MT)). July is the warmest month with temperatures averaging from about 70°F (Marmarth, ND), to about 76°F (Baker, MT). The range of normal average monthly temperatures between the coldest and warmest months is about 55°F. Hourly winds are estimated to average about 11 miles per hour (mph) annually, ranging from about 13 mph during the spring to about 10 mph during the summer. Daytime winds are generally stronger than nighttime and strong storms may bring brief periods of high winds with gusts to more than 50 mph.
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 can continue to early or mid-September. Greenup of cool-season plants may occur in September and October when adequate soil moisture is present.
Table 3. Representative climatic features
Frost-free period (average) | 123 days |
---|---|
Freeze-free period (average) | 140 days |
Precipitation total (average) | 16 in |
Figure 2. Monthly precipitation range
Figure 3. Monthly average minimum and maximum temperature
Influencing water features
No significant water features influence this site.
Soil features
The features common to soils in this site are the loamy fine sand or fine sandy loam textured surface layers and slopes of 6 to 40 percent. The soils in this site are excessively drained and formed in residuum weathered from sandstone. The surface layer is three to five inches thick. The texture of the subsurface layers range from loamy fine sand to fine sand. 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 vegetative barriers. The soil surface is stable and intact.
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.
Access Web Soil Survey (http://websoilsurvey.nrcs.usda.gov/app/HomePage.htm) for specific local soils information.
Table 4. Representative soil features
Surface texture |
(1) Loamy fine sand (2) Fine sandy loam |
---|---|
Family particle size |
(1) Sandy |
Drainage class | Excessively drained |
Permeability class | Moderately rapid |
Soil depth | 10 – 20 in |
Surface fragment cover <=3" | 5% |
Surface fragment cover >3" | 5% |
Available water capacity (0-40in) |
1 – 2 in |
Calcium carbonate equivalent (0-40in) |
10% |
Electrical conductivity (0-40in) |
Not specified |
Sodium adsorption ratio (0-40in) |
Not specified |
Soil reaction (1:1 water) (0-40in) |
6.6 – 8.4 |
Subsurface fragment volume <=3" (Depth not specified) |
5% |
Subsurface fragment volume >3" (Depth not specified) |
5% |
Ecological dynamics
This site developed under Northern Great Plains climatic conditions, natural influences of large herbivores, occasional fire, and other biotic and abiotic factors that typically influence soil/site development. Changes will occur in the plant communities due to short-term weather variations, impacts of native and/or exotic plant and animal species, and management actions. While the following plant community descriptions describe more typical transitions between communities that will occur, severe disturbances, such as periods of well below average precipitation, can cause significant shifts in plant communities and/or species composition.
As this site deteriorates, species such as threadleaf sedge and fringed sagewort will increase. Mid-grasses such as prairie sandreed and little bluestem will decrease in frequency and production.
The plant community upon which interpretations are primarily based is the Prairie Sandreed/Needleandthread/Bluestem Plant Community. This plant community has been determined by studying 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 is a diagram that illustrates the common plant communities that can occur 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
More interactive model formats are also available.
View Interactive Models
More interactive model formats are also available.
View Interactive Models
Click on state and transition labels to scroll to the respective text
Ecosystem states
State 1 submodel, plant communities
State 2 submodel, plant communities
State 1
Reference
The State narrative is under development.
Community 1.1
Prairie Sandreed/Needleandthread/Bluestem
The plant community upon which interpretations are primarily based is the Prairie Sandreed/Needleandthread/Bluestem Plant Community. This is also considered climax. Potential vegetation is about 80 to 90 percent grasses or grass-like plants, 5 to 10 percent forbs, and 5 to 10 percent shrubs. The plant community is a mix of warm- and cool-season grasses. Major grasses include prairie sandreed, needleandthread, and little bluestem. Other significant grasses present include sand bluestem, plains muhly, western wheatgrass, and sedge. The plant community is stable and well adapted to the Northern Great Plains climatic conditions. The diversity in plant species allows for high drought resistance. This is a sustainable plant community (site/soil stability, watershed function, and biologic integrity).
Figure 4. 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 | 770 | 1190 | 1690 |
Shrub/Vine | 65 | 105 | 155 |
Forb | 65 | 105 | 155 |
Total | 900 | 1400 | 2000 |
Figure 5. Plant community growth curve (percent production by month). SD5804, Northern Rolling High Plains, warm-season dominant, cool-season sub-dominant.. Warm-season dominant, cool-season sub-dominant, uplands..
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 | 3 | 7 | 18 | 24 | 25 | 15 | 7 | 1 | 0 | 0 |
Community 1.2
Needleandthread/Sedge
This plant community is the result of continuous season-long grazing. The dominant grass and grass-like species include needleandthread, sedge, prairie sandreed, and blue grama. When compared to the Prairie Sandreed/Needleandthread/Bluestem Plant Community, prairie sandreed, sand bluestem, and little bluestem have decreased. Sedge, needleandthread, and blue grama have increased. This community is well suited to grazing by both domestic livestock and wildlife, during the spring summer and fall. The communities’ soil, biotic integrity and watershed are intact, although more than normal runoff may occur due to the sod forming vegetation.
Figure 6. 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 | 600 | 934 | 1355 |
Forb | 50 | 82 | 120 |
Shrub/Vine | 50 | 82 | 120 |
Moss | 0 | 2 | 5 |
Total | 700 | 1100 | 1600 |
Figure 7. Plant community growth curve (percent production by month). SD5803, Northern Rolling High Plains, cool-season/warm-season co-dominant.. Cool-season, warm-season co-dominant, uplands..
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 | 3 | 10 | 20 | 28 | 21 | 10 | 5 | 3 | 0 | 0 |
Pathway 1.1a
Community 1.1 to 1.2
Continuous season-long grazing will convert the plant community to the Needleandthread/Sedge Plant Community.
Pathway 1.2a
Community 1.2 to 1.1
Prescribed grazing or prescribed burning followed by prescribed grazing will return this plant community to the Prairie Sandreed/Needleandthread/Bluestem Plant Community.
Conservation practices
Prescribed Grazing |
---|
State 2
Sedge
The State narrative is under development.
Community 2.1
Sedge/Clubmoss
This plant community is the result of heavy continuous grazing or continuous seasonal grazing. Mid- and tall cool-season and warm-season grasses have decreased and sedge and blue grama increase along with clubmoss forming a very stable sod condition. Yucca and fringed sagewort have also increased. Total annual production is significantly reduced. The soil is generally well protected on this plant community. The biotic integrity is reduced due to low vegetative production. The sod formed by these grasses is resistant to water infiltration. While this sod protects the site, offsite areas are affected by excessive runoff that may cause gully erosion. This sod is resistant to change and may require practices such as long-term prescribed grazing to return to a mid-/tall grass community.
Figure 8. 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 | 430 | 639 | 1035 |
Forb | 35 | 79 | 128 |
Shrub/Vine | 35 | 79 | 127 |
Moss | 0 | 3 | 10 |
Total | 500 | 800 | 1300 |
Figure 9. Plant community growth curve (percent production by month). SD5802, Northern Rolling High Plains, cool-season dominant, warm-season subdominant. Cool-season dominant, warm-season subdominant..
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 | 3 | 10 | 23 | 34 | 15 | 6 | 5 | 4 | 0 | 0 |
Transition T1
State 1 to 2
Heavy continuous grazing or continuous seasonal grazing (grazing at the same time of year every year with inadequate recovery periods) will convert this plant community to the Sedge/Clubmoss Plant Community.
Restoration pathway R2
State 2 to 1
Long-term prescribed grazing will eventually return this plant community to the Needleandthread/Sedge/Broom Plant Community.
Conservation practices
Prescribed Grazing |
---|
Additional community tables
Table 8. Community 1.1 plant community composition
Group | Common name | Symbol | Scientific name | Annual production (lb/acre) | Foliar cover (%) | |
---|---|---|---|---|---|---|
Grass/Grasslike
|
||||||
1 | Tall Warm-Season Grasses | 280–490 | ||||
prairie sandreed | CALO | Calamovilfa longifolia | 210–420 | – | ||
sand bluestem | ANHA | Andropogon hallii | 28–140 | – | ||
big bluestem | ANGE | Andropogon gerardii | 0–70 | – | ||
2 | Cool-Season Bunch Grasses | 140–280 | ||||
needle and thread | HECOC8 | Hesperostipa comata ssp. comata | 140–280 | – | ||
green needlegrass | NAVI4 | Nassella viridula | 0–70 | – | ||
bluebunch wheatgrass | PSSP6 | Pseudoroegneria spicata | 0–70 | – | ||
3 | Warm-Season Grasses | 70–280 | ||||
little bluestem | SCSC | Schizachyrium scoparium | 70–210 | – | ||
plains muhly | MUCU3 | Muhlenbergia cuspidata | 14–140 | – | ||
Grass, perennial | 2GP | Grass, perennial | 0–70 | – | ||
sideoats grama | BOCU | Bouteloua curtipendula | 0–70 | – | ||
4 | Short-Warm Season Grasses | 28–112 | ||||
blue grama | BOGR2 | Bouteloua gracilis | 14–70 | – | ||
hairy grama | BOHI2 | Bouteloua hirsuta | 14–70 | – | ||
sand dropseed | SPCR | Sporobolus cryptandrus | 14–70 | – | ||
Fendler threeawn | ARPUL | Aristida purpurea var. longiseta | 0–42 | – | ||
5 | Cool-Season Grasses | 70–210 | ||||
western wheatgrass | PASM | Pascopyrum smithii | 28–140 | – | ||
thickspike wheatgrass | ELLAL | Elymus lanceolatus ssp. lanceolatus | 0–70 | – | ||
prairie Junegrass | KOMA | Koeleria macrantha | 14–70 | – | ||
Grass, native | 2GN | Grass, native | 0–70 | – | ||
Scribner's rosette grass | DIOLS | Dichanthelium oligosanthes var. scribnerianum | 14–28 | – | ||
6 | Grass-Likes | 28–140 | ||||
threadleaf sedge | CAFI | Carex filifolia | 28–140 | – | ||
Grass-like (not a true grass) | 2GL | Grass-like (not a true grass) | 14–70 | – | ||
Forb
|
||||||
8 | Forbs | 70–140 | ||||
Forb, native | 2FN | Forb, native | 14–70 | – | ||
field sagewort | ARCA12 | Artemisia campestris | 14–42 | – | ||
white sagebrush | ARLU | Artemisia ludoviciana | 14–42 | – | ||
stiff sunflower | HEPA19 | Helianthus pauciflorus | 14–42 | – | ||
hairy false goldenaster | HEVI4 | Heterotheca villosa | 14–28 | – | ||
blazing star | LIATR | Liatris | 14–28 | – | ||
purple prairie clover | DAPU5 | Dalea purpurea | 14–28 | – | ||
scurfpea | PSORA2 | Psoralidium | 14–28 | – | ||
upright prairie coneflower | RACO3 | Ratibida columnifera | 14–28 | – | ||
goldenrod | SOLID | Solidago | 14–28 | – | ||
scarlet beeblossom | GACO5 | Gaura coccinea | 14–28 | – | ||
American vetch | VIAM | Vicia americana | 14–28 | – | ||
longbract spiderwort | TRBR | Tradescantia bracteata | 0–14 | – | ||
cutleaf anemone | PUPAM | Pulsatilla patens ssp. multifida | 0–14 | – | ||
blacksamson echinacea | ECAN2 | Echinacea angustifolia | 0–14 | – | ||
narrowleaf stoneseed | LIIN2 | Lithospermum incisum | 0–14 | – | ||
rush skeletonplant | LYJU | Lygodesmia juncea | 0–14 | – | ||
purple locoweed | OXLA3 | Oxytropis lambertii | 0–14 | – | ||
beardtongue | PENST | Penstemon | 0–14 | – | ||
spiny phlox | PHHO | Phlox hoodii | 0–14 | – | ||
milkvetch | ASTRA | Astragalus | 0–14 | – | ||
wavyleaf thistle | CIUN | Cirsium undulatum | 0–14 | – | ||
western yarrow | ACMIO | Achillea millefolium var. occidentalis | 0–14 | – | ||
Cuman ragweed | AMPS | Ambrosia psilostachya | 0–14 | – | ||
pussytoes | ANTEN | Antennaria | 0–14 | – | ||
Shrub/Vine
|
||||||
9 | Shrubs | 70–140 | ||||
Shrub (>.5m) | 2SHRUB | Shrub (>.5m) | 0–70 | – | ||
skunkbush sumac | RHTR | Rhus trilobata | 0–42 | – | ||
rose | ROSA5 | Rosa | 14–42 | – | ||
soapweed yucca | YUGL | Yucca glauca | 14–28 | – | ||
western sandcherry | PRPUB | Prunus pumila var. besseyi | 14–28 | – | ||
prairie sagewort | ARFR4 | Artemisia frigida | 14–28 | – | ||
pricklypear | OPUNT | Opuntia | 0–14 | – |
Table 9. Community 1.2 plant community composition
Group | Common name | Symbol | Scientific name | Annual production (lb/acre) | Foliar cover (%) | |
---|---|---|---|---|---|---|
Grass/Grasslike
|
||||||
1 | Tall Warm-Season Grasses | 22–165 | ||||
prairie sandreed | CALO | Calamovilfa longifolia | 22–165 | – | ||
sand bluestem | ANHA | Andropogon hallii | 0–44 | – | ||
big bluestem | ANGE | Andropogon gerardii | 0–33 | – | ||
2 | Cool-Season Bunch Grasses | 165–275 | ||||
needle and thread | HECOC8 | Hesperostipa comata ssp. comata | 165–275 | – | ||
green needlegrass | NAVI4 | Nassella viridula | 0–33 | – | ||
3 | Warm-Season Grasses | 0–55 | ||||
Grass, perennial | 2GP | Grass, perennial | 0–55 | – | ||
plains muhly | MUCU3 | Muhlenbergia cuspidata | 0–55 | – | ||
little bluestem | SCSC | Schizachyrium scoparium | 0–55 | – | ||
sideoats grama | BOCU | Bouteloua curtipendula | 0–33 | – | ||
4 | Short-Warm Season Grasses | 110–220 | ||||
blue grama | BOGR2 | Bouteloua gracilis | 55–165 | – | ||
hairy grama | BOHI2 | Bouteloua hirsuta | 22–88 | – | ||
sand dropseed | SPCR | Sporobolus cryptandrus | 22–88 | – | ||
Fendler threeawn | ARPUL | Aristida purpurea var. longiseta | 11–55 | – | ||
5 | Cool-Season Grasses | 55–110 | ||||
Grass, native | 2GN | Grass, native | 0–55 | – | ||
prairie Junegrass | KOMA | Koeleria macrantha | 11–55 | – | ||
western wheatgrass | PASM | Pascopyrum smithii | 11–55 | – | ||
Scribner's rosette grass | DIOLS | Dichanthelium oligosanthes var. scribnerianum | 11–33 | – | ||
thickspike wheatgrass | ELLAL | Elymus lanceolatus ssp. lanceolatus | 0–33 | – | ||
6 | Grass-Likes | 165–275 | ||||
threadleaf sedge | CAFI | Carex filifolia | 110–220 | – | ||
Grass-like (not a true grass) | 2GL | Grass-like (not a true grass) | 22–110 | – | ||
7 | Non-Native Grasses | 11–55 | ||||
cheatgrass | BRTE | Bromus tectorum | 11–55 | – | ||
bluegrass | POA | Poa | 0–55 | – | ||
Forb
|
||||||
8 | Forbs | 55–110 | ||||
field sagewort | ARCA12 | Artemisia campestris | 11–55 | – | ||
white sagebrush | ARLU | Artemisia ludoviciana | 11–55 | – | ||
Forb, introduced | 2FI | Forb, introduced | 0–55 | – | ||
Forb, native | 2FN | Forb, native | 11–55 | – | ||
scurfpea | PSORA2 | Psoralidium | 11–33 | – | ||
goldenrod | SOLID | Solidago | 11–22 | – | ||
western yarrow | ACMIO | Achillea millefolium var. occidentalis | 0–22 | – | ||
Cuman ragweed | AMPS | Ambrosia psilostachya | 11–22 | – | ||
pussytoes | ANTEN | Antennaria | 0–11 | – | ||
longbract spiderwort | TRBR | Tradescantia bracteata | 0–11 | – | ||
American vetch | VIAM | Vicia americana | 0–11 | – | ||
upright prairie coneflower | RACO3 | Ratibida columnifera | 0–11 | – | ||
milkvetch | ASTRA | Astragalus | 0–11 | – | ||
wavyleaf thistle | CIUN | Cirsium undulatum | 0–11 | – | ||
purple prairie clover | DAPU5 | Dalea purpurea | 0–11 | – | ||
blacksamson echinacea | ECAN2 | Echinacea angustifolia | 0–11 | – | ||
scarlet beeblossom | GACO5 | Gaura coccinea | 0–11 | – | ||
stiff sunflower | HEPA19 | Helianthus pauciflorus | 0–11 | – | ||
hairy false goldenaster | HEVI4 | Heterotheca villosa | 0–11 | – | ||
blazing star | LIATR | Liatris | 0–11 | – | ||
rush skeletonplant | LYJU | Lygodesmia juncea | 0–11 | – | ||
purple locoweed | OXLA3 | Oxytropis lambertii | 0–11 | – | ||
spiny phlox | PHHO | Phlox hoodii | 0–11 | – | ||
Shrub/Vine
|
||||||
9 | Shrubs | 55–110 | ||||
Shrub (>.5m) | 2SHRUB | Shrub (>.5m) | 0–55 | – | ||
prairie sagewort | ARFR4 | Artemisia frigida | 11–55 | – | ||
soapweed yucca | YUGL | Yucca glauca | 11–44 | – | ||
pricklypear | OPUNT | Opuntia | 0–22 | – | ||
skunkbush sumac | RHTR | Rhus trilobata | 0–22 | – | ||
rose | ROSA5 | Rosa | 11–22 | – | ||
western sandcherry | PRPUB | Prunus pumila var. besseyi | 0–11 | – | ||
Moss
|
||||||
10 | Cryptogams | 0–33 | ||||
lesser spikemoss | SEDE2 | Selaginella densa | 0–33 | – |
Table 10. Community 2.1 plant community composition
Group | Common name | Symbol | Scientific name | Annual production (lb/acre) | Foliar cover (%) | |
---|---|---|---|---|---|---|
Grass/Grasslike
|
||||||
1 | Tall Warm-Season Grasses | 0–40 | ||||
prairie sandreed | CALO | Calamovilfa longifolia | 0–40 | – | ||
2 | Cool-Season Bunch Grasses | 8–64 | ||||
needle and thread | HECOC8 | Hesperostipa comata ssp. comata | 8–64 | – | ||
3 | Warm-Season Grasses | 0–16 | ||||
little bluestem | SCSC | Schizachyrium scoparium | 0–16 | – | ||
4 | Short-Warm Season Grasses | 120–200 | ||||
blue grama | BOGR2 | Bouteloua gracilis | 80–160 | – | ||
hairy grama | BOHI2 | Bouteloua hirsuta | 18–80 | – | ||
sand dropseed | SPCR | Sporobolus cryptandrus | 8–80 | – | ||
Fendler threeawn | ARPUL | Aristida purpurea var. longiseta | 8–80 | – | ||
5 | Cool-Season Grasses | 16–64 | ||||
Grass, native | 2GN | Grass, native | 0–40 | – | ||
prairie Junegrass | KOMA | Koeleria macrantha | 8–32 | – | ||
Scribner's rosette grass | DIOLS | Dichanthelium oligosanthes var. scribnerianum | 8–16 | – | ||
western wheatgrass | PASM | Pascopyrum smithii | 0–8 | – | ||
6 | Grass-Likes | 160–320 | ||||
threadleaf sedge | CAFI | Carex filifolia | 120–280 | – | ||
Grass-like (not a true grass) | 2GL | Grass-like (not a true grass) | 40–120 | – | ||
7 | Non-Native Grasses | 8–56 | ||||
cheatgrass | BRTE | Bromus tectorum | 8–56 | – | ||
bluegrass | POA | Poa | 0–40 | – | ||
Forb
|
||||||
8 | Forbs | 40–120 | ||||
Forb, introduced | 2FI | Forb, introduced | 8–56 | – | ||
field sagewort | ARCA12 | Artemisia campestris | 8–56 | – | ||
white sagebrush | ARLU | Artemisia ludoviciana | 16–56 | – | ||
Forb, native | 2FN | Forb, native | 8–40 | – | ||
scurfpea | PSORA2 | Psoralidium | 8–40 | – | ||
western yarrow | ACMIO | Achillea millefolium var. occidentalis | 0–24 | – | ||
Cuman ragweed | AMPS | Ambrosia psilostachya | 8–24 | – | ||
goldenrod | SOLID | Solidago | 8–16 | – | ||
pussytoes | ANTEN | Antennaria | 0–8 | – | ||
milkvetch | ASTRA | Astragalus | 0–8 | – | ||
rush skeletonplant | LYJU | Lygodesmia juncea | 0–8 | – | ||
spiny phlox | PHHO | Phlox hoodii | 0–8 | – | ||
Shrub/Vine
|
||||||
9 | Shrubs | 40–120 | ||||
prairie sagewort | ARFR4 | Artemisia frigida | 16–80 | – | ||
soapweed yucca | YUGL | Yucca glauca | 8–64 | – | ||
pricklypear | OPUNT | Opuntia | 8–32 | – | ||
Shrub (>.5m) | 2SHRUB | Shrub (>.5m) | 0–24 | – | ||
rose | ROSA5 | Rosa | 0–8 | – | ||
Moss
|
||||||
10 | Cryptogams | 0–40 | ||||
lesser spikemoss | SEDE2 | Selaginella densa | 0–40 | – |
Interpretations
Animal community
Animal Community – Wildlife Interpretations
Major Land Resource Area (MLRA) 58D lies within the drier portion of Northern mixed-grass prairie ecosystem where sagebrush steppes to the west yield to grassland steppes to the east. Prior to European settlement, this area consisted of diverse grass/shrub land habitats interspersed with varying densities of depressional, instream wetlands, and woody riparian corridors. These habitats provided critical life cycle components for many of its users. Many species of grassland birds, small mammals, reptiles, 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 small mammal and insect species, were the primary consumers linking the grassland resources to predators such as the wolf, mountain lion, and grizzly bear, as well as, smaller carnivores such as the coyote, bobcat, fox, and raptors. The black-tailed prairie dog was once abundant; however, the species remains a keystone species within its range. The black-footed ferret, burrowing owl, ferruginous hawk, mountain plover, and swift fox were associated with prairie dog complexes.
Historically, the Northern mixed-grass prairie was a disturbance-driven ecosystem with fire, herbivory, and climate functioning 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 impacted plant and animal communities. Bison were historically a keystone species but have been extirpated as a free-ranging herbivore. The loss of the bison, reduction of prairie dog colonies, and loss of fire as ecological drivers greatly influenced the character of the remaining native plant communities and altered wildlife habitats. Human development has reduced habitat quality for area-sensitive species.
Within MLRA 58D, the Shallow Sandy Ecological Site (ES) provides upland grassland cover with an associated forb and shrub component. It was typically part of an expansive grassland landscape that included combinations of Loamy, Shallow Loamy, Shallow Clayey, Thin Loamy, Claypan, Sands, Sandy, Sandy Claypan, Clayey, and Thin Claypan ESs. This site provided habitat for species requiring unfragmented grassland. Important habitat features include 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. Extirpated species include free-ranging bison, grizzly bear, gray wolf, black-footed ferret, mountain plover, Rocky Mountain locust, and swift fox.
The majority of the Shallow Sandy ES remains intact and provides increasingly important habitat for grassland nesting birds, small rodents, coyotes, and a variety of reptiles, amphibians, and insects. Invasive species such as annual bromegrasses and crested wheat have impacted the biological integrity of the site for some grassland birds.
Prairie Sandreed/Needleandthread/Bluestem and Needleandthread/Sedge: The predominance of grasses plus high diversity of forbs and shrubs in this community favors grazers and mixed-feeders, such as deer and pronghorn. Insects, such as pollinators, play a large role in maintaining the forb community and provide a forage base for grassland birds and other species. The complex plant structural diversity provides habitat for a wide array of migratory and resident birds. Grasshopper sparrow, chestnut-collared longspur, Sprague’s pipit, horned lark, lark bunting, and sharp-tailed grouse are common and benefit from the structure and composition this plant community provides. Diverse prey populations are available for grassland raptors such as ferruginous hawk, Swainson’s hawk, golden eagle, and prairie falcon.
The diversity of grasses, forbs, and shrubs provide high nutrition levels for small and large herbivores including voles, mice, thirteen-lined ground squirrel, white-tailed jackrabbit, and deer. The higher stature of this plant community provides thermal, protective, and escape cover for herbivores and grassland birds. Predators utilizing this plant community include coyote, American badger, red fox, and long-tailed weasel. This plant community provides habitat for herptiles such as the spade foot toad, bull snake, and western rattlesnake.
Resulting from continuous season-long grazing, the warm-season grass component has been substantially reduced and a shift to a needleandthread and sedge community occurs. The forb and shrub diversity has not substantially decreased. The shift from the HCPC to the needleandthread/sedge community does not result in a significant change to the wildlife community.
Sedge/Clubmoss: Resulting from heavy, continuous grazing or continuous seasonal grazing sedges and clubmoss will dominate. The decrease in diversity of grasses, forbs, and shrubs will result in less seed production or lower quality nutrition for small herbivores including voles, mice, and thirteen-lined ground squirrel. Species such as horned lark, upland sandpiper, and white-tailed jackrabbit will increase due to the loss of the tall grass component.
The short stature of this plant community limits suitable thermal, protective, and escape cover. Prey populations are reduced and are more vulnerable to raptor and mammalian predation. Predators utilizing this plant community include the coyote, American badger, red fox, and long-tailed weasel.
Extreme impairment of the ecological processes impacts offsite aquatic habitats through excessive runoff, nutrient, and sediment loads. Elevated surface temperatures resulting from reduced cover and litter will greatly reduce habitat for most amphibian species, grassland birds, and mammals.
Animal Community – Grazing Interpretations
As this site improves in condition through proper management (from the more shortgrass dominated plant communities to the interpretive plant community), the advantage for livestock production includes: higher forage production, improved summer forage production, and higher water infiltration. The Sedge/Clubmoss Plant Community is of limited value for livestock production.
Grazing by domestic livestock is one of the major income-producing industries in the area. Rangeland in this area may provide yearlong forage. During the dormant period, the forage for livestock will likely be lacking protein to meet livestock requirements, and added protein will allow 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 C. Infiltration and runoff potential for this site varies from moderate to high depending on 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 exception would be where shortgrasses form a strong sod and dominate the site. Normally, areas where ground cover is less than 50 percent have the greatest potential to have reduced infiltration and higher runoff (refer to Section 4, NRCS National Engineering Handbook for runoff quantities and hydrologic curves).
Recreational uses
This site provides hunting opportunities for upland game species. The wide varieties of plants which bloom from spring until fall have an esthetic value that appeals to visitors.
Wood products
No appreciable wood products are typically present on this site.
Other products
Seed harvest of native plant species can provide additional income on this site.
Supporting information
Inventory data references
Information presented here has been derived from NRCS clipping data and other inventory data. Field observations and experience were also used. Those involved in developing this site description include: Ryan Beer, Range Management Specialist (RMS), NRCS; Stan Boltz, RMS, NRCS; Dave Dewald, Wildlife BIO, NRCS; Jody Forman, RMS, NRCS; Dennis Froemke, RMS, NRCS; Cheryl Nielsen, RMS, NRCS; Jeff Printz, RMS, NRCS; Mike Stirling, RMS, NRCS; and Darrell Vanderbusch, Soil Scientist, NRCS.
Other references
High Plains Regional Climate Center, University of Nebraska, 830728 Chase Hall, Lincoln, NE 68583-0728. (http://www.hprcc.unl.edu/)
USDA, NRCS. National Water and Climate Center, 101 SW Main, Suite 1600, Portland, OR 97204-3224. (http://www.wcc.nrcs.usda.gov/)
USDA, NRCS. National Range and Pasture Handbook, September 1997
USDA, NRCS. National Soil Information System, Information Technology Center, 2150 Centre Avenue, Building A, Fort Collins, CO 80526. (http://nasis.nrcs.usda.gov)
USDA, NRCS. 2001. The PLANTS Database, Version 3.1 (http://plants.usda.gov). National Plant Data Center, Baton Rouge, LA 70874-4490 USA
USDA, NRCS, Various Published Soil Surveys
Contributors
Stan Boltz
Travis Patient
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, Ryan Beer, Mitch Iverson, Thad Berrett, Cheryl Nielsen |
---|---|
Contact for lead author | stanley.boltz@sd.usda.gov, 605-352-1236 |
Date | 05/07/2010 |
Approved by | Stan Boltz |
Approval date | |
Composition (Indicators 10 and 12) based on | Annual Production |
Indicators
-
Number and extent of rills:
None. -
Presence of water flow patterns:
None, or barely visible and discontinuous when present. -
Number and height of erosional pedestals or terracettes:
Few pedestalled plants typically on steeper slopes. -
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
0 to 15 percent is typical -
Number of gullies and erosion associated with gullies:
None should be present. -
Extent of wind scoured, blowouts and/or depositional areas:
None. -
Amount of litter movement (describe size and distance expected to travel):
Very little litter movement of smallest size class. -
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
Soil aggregate stability ratings should typically be 5 to 6, normally 6. Surface organic matter adheres to the soil surface. Soil surface fragments (peds) 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 3 to 5 inches thick with light grayish brown colors. Structure should typically be fine granular at least in the upper A-horizon. -
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
Combination of shallow & deep rooted species (mid & tall rhizomatous and tufted perennial cool- and warm-season grasses) with fine & coarse roots positively influence infiltration. -
Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on this site):
None. -
Functional/Structural Groups (list in order of descending dominance by above-ground annual-production or live foliar cover using symbols: >>, >, = to indicate much greater than, greater than, and equal to):
Dominant:
Tall warm-season rhizomatous grasses >> Mid/tall cool-season bunchgrasses = Mid warm-season grasses >Sub-dominant:
Mid/short cool-season grasses >Other:
Grass-likes = Forbs = Shrubs > Short warm-season grassesAdditional:
-
Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
Very little evidence of decadence or mortality. Bunch grasses have strong, healthy centers and shrubs are vigorous. -
Average percent litter cover (%) and depth ( in):
-
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
Production ranges from 900-2,000 lbs./acre (air-dry weight). Reference value production is 1,400 lbs./acre (air-dry weight). -
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:
State and local noxious weeds -
Perennial plant reproductive capability:
All species exhibit high vigor relative to climatic conditions. Do not rate based solely on seed production. Perennial grasses should have vigorous rhizomes or tillers.
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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.
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