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Conservation Service

Ecological site R053BY026ND

Sandy Claypan

Last updated: 1/11/2024
Accessed: 12/04/2024

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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.

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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: 42a – Missouri Coteau; 42b – Collapsed Glacial Outwash; 42c – Missouri Coteau Slope; 42d – Northern Missouri Coteau; 42f – Southern Missouri Coteau Slope; 42g – Ponca Plains; and 42h – Southern River Breaks.

Associated sites

R053BY007ND	Sands
R053BY013ND	Thin Claypan
R053BY018ND	Linear Meadow

R053BY007ND

Sands

R053BY013ND

Thin Claypan

R053BY018ND

Linear Meadow

Similar sites

R053BY002ND	Claypan [Well drained soils on uplands or terraces that don’t receive extra moisture with a dense sodic subsoil below 6 inches with salts below 16 inches. Indicator species are western wheatgrass, blue grama, heath aster, western yarrow and fringed sagewort. This site has less production, no prairie sandreed and little threadleaf sedge, more blue grama and Sandberg’s bluegrass, soil texture is finer but with similar sodic subsoils layer.]
R053BY008ND	Sandy [Does not receive additional moisture. Found on dry uplands upslope from Loamy Overflow site, down slope from Thin Upland or Shallow Loamy sites. Similar landscape position as Loamy, Sands, Clayey sites; will ribbon up to 1 inches. Indicator species are prairie sandreed with western wheatgrass and green needlegrass intermixed. This site doesn’t have dense sodic subsoil below 6 inches with salts below 16 inches, far less western wheatgrass, blue grama, more prairie sandreed, and sand bluestem, more production.]

R053BY002ND

Claypan

[Well drained soils on uplands or terraces that don’t receive extra moisture with a dense sodic subsoil below 6 inches with salts below 16 inches. Indicator species are western wheatgrass, blue grama, heath aster, western yarrow and fringed sagewort. This site has less production, no prairie sandreed and little threadleaf sedge, more blue grama and Sandberg’s bluegrass, soil texture is finer but with similar sodic subsoils layer.]

R053BY008ND

Sandy

[Does not receive additional moisture. Found on dry uplands upslope from Loamy Overflow site, down slope from Thin Upland or Shallow Loamy sites. Similar landscape position as Loamy, Sands, Clayey sites; will ribbon up to 1 inches. Indicator species are prairie sandreed with western wheatgrass and green needlegrass intermixed. This site doesn’t have dense sodic subsoil below 6 inches with salts below 16 inches, far less western wheatgrass, blue grama, more prairie sandreed, and sand bluestem, more production.]

Table 1. Dominant plant species

Tree	Not specified
Shrub	Not specified
Herbaceous	(1) Pascopyrum smithii (2) Hesperostipa comata ssp. comata

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Physiographic features

This site occurs on nearly level to rolling uplands.

Table 2. Representative physiographic features

Landforms	(1) Outwash plain (2) Till plain (3) Delta plain
Flooding frequency	None
Ponding frequency	None
Elevation	488 – 610 m
Slope	0 – 3%
Water table depth	107 – 203 cm
Aspect	Aspect is not a significant factor

Climatic features

MLRA 53B is considered to have a continental climate – cold winters and hot summers, low humidity, light rainfall, and much sunshine. Extremes in temperature are characteristic. The climate is the result of this MLRA’s location in the geographic center of North America. There are few natural barriers on the northern Great Plains. The air masses move unobstructed across the plains and account for rapid changes in temperature.

Annual precipitation ranges from 15 to 20 inches per year. The normal average annual temperature is about 41° F. January is the coldest month with average temperatures ranging from about 4° F (Powers Lake, ND) to about 10° F (Pollock, SD). July is the warmest month with temperatures averaging from about 67° F (Powers Lake, ND) to about 72° F (Pollock, SD). The range of normal average monthly temperatures between the coldest and warmest months is about 62° F. This large annual range attests to the continental nature of this MLRA's climate. Winds 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 and occasional strong storms may bring brief periods of high winds with gusts to more than 50 miles per hour.

Growth of native cool-season plants begins in late March and continues to early to mid July. Native warm-season plants begin growth in mid May and continue to the end of August. Green up of cool-season plants can occur in September and October when adequate soil moisture is present.

Table 3. Representative climatic features

Frost-free period (average)	142 days
Freeze-free period (average)	122 days
Precipitation total (average)	457 mm

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Figure 2. Monthly precipitation range

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Line

Figure 3. Monthly average minimum and maximum temperature

Figure 4. Annual precipitation pattern

Figure 5. Annual average temperature pattern

Soil features

These are moderately deep to very deep, moderately well drained soils. They have moderately coarse to medium textured surface layers underlain by a sodic subsoil. The subsoils are moderately coarse to medium textured and are high in sodium. Saturated hydraulic conductivity is moderate to slow and available water capacity is moderate. Salinity is none to slight and sodicity is high. This site is on nearly level to gently sloping outwash plains, till plains and delta plains. Slope ranges from 0 to 3 percent. 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. Sub-surface soil layers are restrictive to water movement and root penetration.

Major soil series correlated to this ecological site can be found in Section II of the Natural Resources Conservation Service Field Office Technical Guide or the following web sites:
http://www.nrcs.usda.gov/technical/efotg/

Table 4. Representative soil features

Surface texture	(1) Fine sandy loam
Family particle size	(1) Loamy
Drainage class	Moderately well drained
Permeability class	Slow to moderate
Soil depth	20 – 51 cm
Surface fragment cover <=3"	0%
Surface fragment cover >3"	0%
Available water capacity (0-101.6cm)	5.08 – 7.62 cm
Calcium carbonate equivalent (0-101.6cm)	0 – 20%
Electrical conductivity (0-101.6cm)	0 – 8 mmhos/cm
Sodium adsorption ratio (0-101.6cm)	0 – 15
Soil reaction (1:1 water) (0-101.6cm)	5.1 – 9
Subsurface fragment volume <=3" (Depth not specified)	0 – 5%
Subsurface fragment volume >3" (Depth not specified)	0%

Ecological dynamics

The site developed under Northern Great Plains climatic conditions, and included natural influence of large herbivores and occasional fire. Changes will occur in the plant communities due to climatic conditions and/or management actions. Due to the nature of the soils, the site is considered quite fragile. Under continued adverse impacts, a rapid decline in vegetative vigor and composition will occur. Under favorable vegetative management treatments the site can slowly return to the Historic Climax Plant Community (HCPC).

The plant community upon which interpretations are primarily based is the HCPC. The HCPC 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. Subclimax plant communities, states, transitional pathways, and thresholds have been determined through similar studies and experience.

Continuous grazing without adequate recovery periods following each grazing occurrence over several years causes this site to depart from the HCPC. Species such as western wheatgrass, blue grama, sedges, cudweed sagewort, hairy golden aster, prairie coneflower, scurfpea and fringed sagewort will initially increase. Prairie sandreed, sand bluestem green needlegrass, false gromwell, vetch, penstemon and leadplant will decrease in frequency and production. In time, heavy continuous grazing will likely cause upland sedges and blue grama to dominate and pioneer perennials and annuals to increase. The resulting plant community is relatively stable and the competitive advantage prevents other species from establishing.

Extended periods of non-use and/or lack of fire will result in a plant community having high litter levels, which favors an increase in Kentucky bluegrass and/or smooth bromegrass, and in time, shrubs such as western snowberry will increase.

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 will be discussed in more detail in the plant community descriptions following the diagram.

State and transition model

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Standard diagram

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State 1
Western Wheatgrass/Tall Warm-Season (HCPC)

Community 1.1
Western Wheatgrass/Tall Warm-Season (HCPC)

This is the interpretive plant community and is considered to be the Historic Climax Plant Community (HCPC). This community evolved with grazing by large herbivores and occasional prairie fire. It is well suited for grazing by domestic livestock and can be found on areas that are properly managed with prescribed grazing that allows for proper utilization, changes in season of use and adequate recovery periods following each grazing event. The potential vegetation is about 85% grasses or grass-like plants, 10% forbs, and 5% shrubs. Cool-season and tall warm-season grasses dominate the plant community. The co-dominant grasses include western wheatgrass and prairie sandreed. Other grasses and grass-like plants occurring on the site include needleandthread, green needlegrass, blue grama, sand bluestem, prairie junegrass and sedges. Significant forbs include stiff sunflower, false gromwell, silverleaf scurfpea, western yarrow and goldenrod. In many areas western snowberry is the principle shrub and occurs in patchy mosaic. Other shrubs include prairie rose, leadplant and fringed sagewort. 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). Community dynamics, nutrient cycle, water cycle and energy flow are functioning properly. Plant litter is properly distributed with very little movement off-site and natural plant mortality is very low. The diversity in plant species allows for high drought tolerance. Low available water capacity coupled with high accumulations of sodium and slow permeability strongly influences the soil-water-plant relationship.

Figure 6. Annual production by plant type (representative values) or group (midpoint values)

Table 5. Annual production by plant type

Plant type	Low (kg/hectare)	Representative value (kg/hectare)	High (kg/hectare)
Grass/Grasslike	1653	2207	2757
Forb	118	185	252
Shrub/Vine	22	74	129
Total	1793	2466	3138

Figure 7. Plant community growth curve (percent production by month). ND5303, Missouri Coteau, 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
0	0	2	6	21	40	20	6	4	1	0	0

State 2
Blue Grama/Sedge/Western Wheatgrass

Community 2.1
Blue Grama/Sedge/Western Wheatgrass

This plant community can quickly develop from the adverse effects of heavy, continuous grazing and/or annual, early spring seasonal grazing. Annual grazing too early in the spring depletes stored carbohydrates, resulting in weakening and eventual death of the cool season mid-grasses. Short grasses and grass-likes and forbs increase to dominate the site and annual production decreases dramatically. Lack of litter and reduced plant vigor result in higher soil temperatures, poor water infiltration rates, and high evapotranspiration, which gives blue grama and sedges a competitive advantage over cool season mid-grasses. This plant community can occur throughout the pasture, on spot grazed areas, and around water sources where season-long grazing patterns occur. Blue grama, sedges and western wheatgrass are the dominant species. Other grasses that may be present include red threeawn, needleandthread, prairie junegrass and annual grasses. Forbs such as hairy goldaster, cudweed sagewort, heath aster, Lambert crazyweed, prairie coneflower, scurfpea and western yarrow may also be present. There is usually less than 10% bare ground. This plant community is relatively stable. The thick sod and competitive advantage prevents other species from establishing. This plant community is less productive than the HCPC. Runoff increases and infiltration will decrease. Soil erosion will be minimal due to the sod forming habit of blue grama.

Figure 8. 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	549	1143	1737
Shrub/Vine	62	101	140
Forb	62	101	140
Total	673	1345	2017

Figure 9. Plant community growth curve (percent production by month). ND5303, Missouri Coteau, 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
0	0	2	6	21	40	20	6	4	1	0	0

State 3
Low Plant Density, Excessive Litter

Community 3.1
Low Plant Density, Excessive Litter

This plant community develops after an extended period of 15 or more years of non-use by herbivores and exclusion of fire. This plant community can be dispersed throughout the pasture, encircling spot grazed areas, and areas distant from water sources. This is a typical pattern found in properly stocked pastures grazed season-long. Plant litter accumulates in large amounts as this community develops. Litter buildup reduces plant vigor and density, and seedling recruitment declines. Eventually litter levels become abundant enough to crowd out living plants and reduce plant density. Annual and/or biennial forbs and annual grasses commonly fill these interspaces. Due to a lack of tiller stimulation and sunlight, native bunchgrasses typically develop dead centers and native rhizomatous grasses are limited to small colonies. Heavy litter covers shorter understory species (i.e. short grasses and sedges) restricting their ability to capture adequate sunlight for photosynthesis. Vigor and diversity of native plants are reduced. Non-native grasses, such as Kentucky bluegrass, crested wheatgrass, smooth bromegrass and cheatgrass tend to dominant this plant community. Other grasses that may be present include western wheatgrass, needleandthread, green needlegrass and Sandberg bluegrass. The common forbs include sweetclover, green sagewort, cudweed sagewort and heath aster. Fringed sagewort and snowberry are the principal shrubs and tend to increase in density and cover. This plant community is resistant to change without prescribed grazing or fire. The combination of both grazing and fire is most effective in moving this plant community towards the HCPC. Soil erosion is low. Compared to the HCPC, infiltration is reduced to the lower root zone. Runoff is similar to the HCPC. This plant community tends to be moisture loving and usually tends to utilize the spring moisture quickly causing forage base to become dry and not very palatable early in the summer. Once this plant community is reached, time and external resources will be needed to see any immediate recovery in the diversity of the site.

Figure 10. Annual production by plant type (representative values) or group (midpoint values)

Table 7. Annual production by plant type

Plant type	Low (kg/hectare)	Representative value (kg/hectare)	High (kg/hectare)
Grass/Grasslike	1166	1620	2186
Shrub/Vine	90	142	196
Forb	90	143	196
Total	1346	1905	2578

Figure 11. Plant community growth curve (percent production by month). ND5301, Missouri Coteau, 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
0	0	3	8	24	45	10	3	5	2	0	0

Additional community tables

Table 8. Community 1.1 plant community composition

Group	Common name	Symbol	Scientific name	Annual production (kg/hectare)	Foliar cover (%)
Grass/Grasslike
1	Western Wheatgrass			370–616
	western wheatgrass	PASM	Pascopyrum smithii	370–616	–
2	Tall Warm-Season Grasses			247–370
	prairie sandreed	CALO	Calamovilfa longifolia	123–247	–
	sand bluestem	ANHA	Andropogon hallii	74–173	–
	big bluestem	ANGE	Andropogon gerardii	0–74	–
3	Needlegrass			247–370
	needle and thread	HECOC8	Hesperostipa comata ssp. comata	247–370	–
	green needlegrass	NAVI4	Nassella viridula	49–123	–
4	Grama			123–247
	blue grama	BOGR2	Bouteloua gracilis	123–247	–
5	Other Native Grasses			123–247
	slender wheatgrass	ELTR7	Elymus trachycaulus	49–197	–
	little bluestem	SCSC	Schizachyrium scoparium	0–74	–
	Fendler threeawn	ARPUL	Aristida purpurea var. longiseta	0–74	–
	prairie Junegrass	KOMA	Koeleria macrantha	25–49	–
	Grass, perennial	2GP	Grass, perennial	25–49	–
	sand dropseed	SPCR	Sporobolus cryptandrus	0–25	–
	Scribner's rosette grass	DIOLS	Dichanthelium oligosanthes var. scribnerianum	0–25	–
6	Grass-Likes			123–247
	threadleaf sedge	CAFI	Carex filifolia	123–197	–
	sun sedge	CAINH2	Carex inops ssp. heliophila	49–123	–
	Grass-like (not a true grass)	2GL	Grass-like (not a true grass)	0–25	–
Forb
8	Forbs			123–247
	Forb, perennial	2FP	Forb, perennial	0–74	–
	western yarrow	ACMIO	Achillea millefolium var. occidentalis	25–49	–
	stiff sunflower	HEPA19	Helianthus pauciflorus	25–49	–
	scurfpea	PSORA2	Psoralidium	25–49	–
	upright prairie coneflower	RACO3	Ratibida columnifera	0–25	–
	goldenrod	SOLID	Solidago	0–25	–
	scarlet globemallow	SPCO	Sphaeralcea coccinea	0–25	–
	white heath aster	SYER	Symphyotrichum ericoides	0–25	–
	longbract spiderwort	TRBR	Tradescantia bracteata	0–25	–
	American vetch	VIAM	Vicia americana	0–25	–
	purple locoweed	OXLA3	Oxytropis lambertii	0–25	–
	beardtongue	PENST	Penstemon	0–25	–
	spiny phlox	PHHO	Phlox hoodii	0–25	–
	hairy false goldenaster	HEVI4	Heterotheca villosa	0–25	–
	blazing star	LIATR	Liatris	0–25	–
	rush skeletonplant	LYJU	Lygodesmia juncea	0–25	–
	tarragon	ARDR4	Artemisia dracunculus	0–25	–
	white sagebrush	ARLU	Artemisia ludoviciana	0–25	–
	milkvetch	ASTRA	Astragalus	0–25	–
	wavyleaf thistle	CIUN	Cirsium undulatum	0–25	–
	prairie clover	DALEA	Dalea	0–25	–
	blacksamson echinacea	ECAN2	Echinacea angustifolia	0–25	–
	sanddune wallflower	ERCAC	Erysimum capitatum var. capitatum	0–25	–
	scarlet beeblossom	GACO5	Gaura coccinea	0–25	–
Shrub/Vine
9	Shrubs			25–123
	Subshrub (<.5m)	2SUBS	Subshrub (<.5m)	0–49	–
	leadplant	AMCA6	Amorpha canescens	25–49	–
	prairie sagewort	ARFR4	Artemisia frigida	25–49	–
	rose	ROSA5	Rosa	25–49	–
	western snowberry	SYOC	Symphoricarpos occidentalis	25–49	–
	pricklypear	OPUNT	Opuntia	0–25	–

Table 9. Community 2.1 plant community composition

Group	Common name	Symbol	Scientific name	Annual production (kg/hectare)	Foliar cover (%)
Grass/Grasslike
1	Western Wheatgrass			67–202
	western wheatgrass	PASM	Pascopyrum smithii	67–202	–
2	Tall Warm-Season Grasses			13–67
	prairie sandreed	CALO	Calamovilfa longifolia	13–67	–
3	Needlegrass			27–108
	needle and thread	HECOC8	Hesperostipa comata ssp. comata	27–108	–
	green needlegrass	NAVI4	Nassella viridula	0–13	–
4	Grama			135–269
	blue grama	BOGR2	Bouteloua gracilis	135–269	–
5	Other Native Grasses			40–161
	Fendler threeawn	ARPUL	Aristida purpurea var. longiseta	13–67	–
	Grass, perennial	2GP	Grass, perennial	0–54	–
	sand dropseed	SPCR	Sporobolus cryptandrus	13–54	–
	slender wheatgrass	ELTR7	Elymus trachycaulus	0–40	–
	prairie Junegrass	KOMA	Koeleria macrantha	13–27	–
	Scribner's rosette grass	DIOLS	Dichanthelium oligosanthes var. scribnerianum	13–27	–
6	Grass-Likes			67–202
	threadleaf sedge	CAFI	Carex filifolia	67–202	–
	sun sedge	CAINH2	Carex inops ssp. heliophila	27–67	–
	Grass-like (not a true grass)	2GL	Grass-like (not a true grass)	0–40	–
7	Non-Native Grasses			13–67
	smooth brome	BRIN2	Bromus inermis	0–67	–
	Kentucky bluegrass	POPR	Poa pratensis	13–67	–
	cheatgrass	BRTE	Bromus tectorum	0–54	–
	crested wheatgrass	AGCR	Agropyron cristatum	0–40	–
Forb
8	Forbs			67–135
	Forb, annual	2FA	Forb, annual	0–67	–
	Forb, perennial	2FP	Forb, perennial	0–67	–
	tarragon	ARDR4	Artemisia dracunculus	13–40	–
	white sagebrush	ARLU	Artemisia ludoviciana	13–40	–
	scurfpea	PSORA2	Psoralidium	13–40	–
	goldenrod	SOLID	Solidago	13–40	–
	upright prairie coneflower	RACO3	Ratibida columnifera	13–27	–
	blazing star	LIATR	Liatris	13–27	–
	western yarrow	ACMIO	Achillea millefolium var. occidentalis	13–27	–
	prairie clover	DALEA	Dalea	13–27	–
	white heath aster	SYER	Symphyotrichum ericoides	13–27	–
	sanddune wallflower	ERCAC	Erysimum capitatum var. capitatum	0–13	–
	milkvetch	ASTRA	Astragalus	0–13	–
	wavyleaf thistle	CIUN	Cirsium undulatum	0–13	–
	rush skeletonplant	LYJU	Lygodesmia juncea	0–13	–
	purple locoweed	OXLA3	Oxytropis lambertii	0–13	–
	beardtongue	PENST	Penstemon	0–13	–
	spiny phlox	PHHO	Phlox hoodii	0–13	–
	scarlet globemallow	SPCO	Sphaeralcea coccinea	0–13	–
Shrub/Vine
9	Shrubs			67–135
	prairie sagewort	ARFR4	Artemisia frigida	13–67	–
	rose	ROSA5	Rosa	13–54	–
	western snowberry	SYOC	Symphoricarpos occidentalis	13–40	–
	pricklypear	OPUNT	Opuntia	0–40	–
	Subshrub (<.5m)	2SUBS	Subshrub (<.5m)	0–40	–

Table 10. Community 3.1 plant community composition

Group	Common name	Symbol	Scientific name	Annual production (kg/hectare)	Foliar cover (%)
Grass/Grasslike
1	Western Wheatgrass			95–191
	western wheatgrass	PASM	Pascopyrum smithii	95–191	–
2	Tall Warm-Season Grasses			19–95
	prairie sandreed	CALO	Calamovilfa longifolia	19–95	–
	sand bluestem	ANHA	Andropogon hallii	0–19	–
3	Needlegrass			38–191
	needle and thread	HECOC8	Hesperostipa comata ssp. comata	38–191	–
	green needlegrass	NAVI4	Nassella viridula	0–95	–
4	Grama			19–95
	blue grama	BOGR2	Bouteloua gracilis	19–95	–
5	Other Native Grasses			95–286
	slender wheatgrass	ELTR7	Elymus trachycaulus	19–133	–
	Fendler threeawn	ARPUL	Aristida purpurea var. longiseta	19–95	–
	sand dropseed	SPCR	Sporobolus cryptandrus	19–95	–
	Grass, perennial	2GP	Grass, perennial	0–76	–
	Scribner's rosette grass	DIOLS	Dichanthelium oligosanthes var. scribnerianum	19–38	–
	prairie Junegrass	KOMA	Koeleria macrantha	19–38	–
	little bluestem	SCSC	Schizachyrium scoparium	0–19	–
6	Grass-Likes			57–191
	threadleaf sedge	CAFI	Carex filifolia	38–191	–
	sun sedge	CAINH2	Carex inops ssp. heliophila	19–57	–
	Grass-like (not a true grass)	2GL	Grass-like (not a true grass)	0–57	–
7	Non-Native Grasses			286–476
	Kentucky bluegrass	POPR	Poa pratensis	95–381	–
	smooth brome	BRIN2	Bromus inermis	38–286	–
	cheatgrass	BRTE	Bromus tectorum	19–191	–
	crested wheatgrass	AGCR	Agropyron cristatum	0–95	–
Forb
8	Forbs			95–191
	Forb, perennial	2FP	Forb, perennial	0–152	–
	Forb, annual	2FA	Forb, annual	0–95	–
	white sagebrush	ARLU	Artemisia ludoviciana	19–95	–
	tarragon	ARDR4	Artemisia dracunculus	19–76	–
	scurfpea	PSORA2	Psoralidium	19–57	–
	goldenrod	SOLID	Solidago	19–57	–
	white heath aster	SYER	Symphyotrichum ericoides	19–57	–
	upright prairie coneflower	RACO3	Ratibida columnifera	19–38	–
	blazing star	LIATR	Liatris	19–38	–
	western yarrow	ACMIO	Achillea millefolium var. occidentalis	19–38	–
	prairie clover	DALEA	Dalea	19–38	–
	blacksamson echinacea	ECAN2	Echinacea angustifolia	0–19	–
	sanddune wallflower	ERCAC	Erysimum capitatum var. capitatum	0–19	–
	scarlet beeblossom	GACO5	Gaura coccinea	0–19	–
	rush skeletonplant	LYJU	Lygodesmia juncea	0–19	–
	purple locoweed	OXLA3	Oxytropis lambertii	0–19	–
	beardtongue	PENST	Penstemon	0–19	–
	milkvetch	ASTRA	Astragalus	0–19	–
	wavyleaf thistle	CIUN	Cirsium undulatum	0–19	–
	scarlet globemallow	SPCO	Sphaeralcea coccinea	0–19	–
Shrub/Vine
9	Shrubs			95–191
	prairie sagewort	ARFR4	Artemisia frigida	19–95	–
	rose	ROSA5	Rosa	19–95	–
	western snowberry	SYOC	Symphoricarpos occidentalis	19–95	–
	Subshrub (<.5m)	2SUBS	Subshrub (<.5m)	0–38	–
	pricklypear	OPUNT	Opuntia	0–19	–

Interpretations

Animal community

Wildlife Interpretations:
Under development.

Grazing Interpretations:
This site is well adapted to managed grazing by domestic livestock. The predominance of herbaceous plants across all plant community phases best lends these sites to grazing by cattle but other domestic grazers with differing diet preferences may also be a consideration depending upon management objectives. Often, the current plant community does not entirely match any particular plant community (as described in the ecological site description). Because of this, a resource inventory is necessary to document plant composition and production. Proper interpretation of this inventory data will permit the establishment of a safe, initial stocking rate for the type and class of animals and level of grazing management. More accurate stocking rate estimates should eventually be calculated using actual stocking rate information and monitoring data.

Hydrological functions

Water is the principal factor limiting herbage production on this site. The site is dominated by soils in hydrologic group D. Infiltration varies from moderate to slow and runoff potential varies from medium to high depending on soil hydrologic group and ground cover. In many cases, areas with greater than 75% ground cover have the greatest potential for high infiltration and lower runoff. An exception would be where short grasses form a dense sod and dominate the site. Areas where ground cover is less than 50% 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 variety of plants which bloom from spring until fall have an esthetic value that appeals to visitors.

Wood products

No appreciable wood products are present on the 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 and other inventory data. Also, field knowledge of range-trained personnel was used. All descriptions were peer reviewed and/or field-tested by various private, state and federal agency specialists. Those involved in developing this site description include: Stan Boltz, NRCS Range Management Specialist; Michael D. Brand, State Land Dept., Director Surface Management; David Dewald, NRCS State Biologist; Paul Drayton, NRCS District Conservationist; Jody Forman, NRCS Range Management Specialist; Dennis Froemke, NRCS Range Management Specialist; Jeff Printz, NRCS State Range Management Specialist; Josh Saunders, NRCS Range Management Specialist; Kevin Sedivec, Extension Rangeland Management Specialist; Darrell Vanderbusch, NRCS Resource Soil Scientist; and Lee Voigt, NRCS Range Management Specialist.
Data Source Number of Records Sample Period State County
SCS-RANGE-417
Ocular Estimate 1 2003 SD McPherson

Other references

High Plains Regional Climate Center, University of Nebraska, 830728 Chase Hall, Lincoln, NE 68583-0728. (http://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

Jeff Printz
Jeff Printz/Stan Boltz

Approval

Suzanne Mayne-Kinney, 1/11/2024

Rangeland health reference sheet

Interpreting Indicators of Rangeland Health is a qualitative assessment protocol used to determine ecosystem condition based on benchmark characteristics described in the Reference Sheet. A suite of 17 (or more) indicators are typically considered in an assessment. The ecological site(s) representative of an assessment location must be known prior to applying the protocol and must be verified based on soils and climate. Current plant community cannot be used to identify the ecological site.

Author(s)/participant(s)	Jeff Printz, Stan Boltz, Lee Voigt, Jody Forman
Contact for lead author	Jeff.printz@nd.usda.gov 701-530-2080
Date	03/02/2012
Approved by	Suzanne Mayne-Kinney
Approval date
Composition (Indicators 10 and 12) based on	Annual Production

Indicators

Number and extent of rills:
None.
Presence of water flow patterns:
None.
Number and height of erosional pedestals or terracettes:
None.
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
Bare ground is 5 to 20 percent. Patch size is 2 inches or less and not connected.
Number of gullies and erosion associated with gullies:
None.
Extent of wind scoured, blowouts and/or depositional areas:
None.
Amount of litter movement (describe size and distance expected to travel):
None.
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
Average 5 to 6. 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):
Use soil series description for depth, color and structure of A horizon/surface layer.
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 & tall rhizomatous and tufted perennial cool- and warm-season grasses) with fine and coarse roots positively influences infiltration.
Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on this site):
No compaction layer evident. Naturally occurring compaction layer (“claypan”) and some platy surface structure is expected for this site.
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:
Mid, cool-season rhizomatous grasses >

Sub-dominant:
Tall, warm-season grasses = mid, cool-season bunchgrasses

Other:
Short, warm-season grasses = grass-likes = forbs > shrubs > short, cool-season grasses = mid, warm-season grasses

Additional:
Due to differing root structure and distribution, Kentucky bluegrass and smooth bromegrass do not fit into reference plant community F/S groups.
Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
No plant mortality or decadence expected.
Average percent litter cover (%) and depth ( in):
Plant litter is in contact with soil surface.
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
Representative value = 2200 lbs./ac air dry with a range of 1600 to 2800 lbs./ac air dry depending upon growing conditions.
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, Kentucky bluegrass, smooth bromegrass
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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Natural ResourcesConservation Service

Ecological site R053BY026ND

Sandy Claypan

Last updated: 1/11/2024 Accessed: 12/04/2024

General information

Figure 1. Mapped extent

Classification relationships

Associated sites

Similar sites

Table 1. Dominant plant species

Ecosystem states

State 1 submodel, plant communities

State 2 submodel, plant communities

State 3 submodel, plant communities

Natural Resources
Conservation Service

Last updated: 1/11/2024
Accessed: 12/04/2024