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Ecological site R053BY007ND

Sands

Last updated: 1/11/2024
Accessed: 12/21/2024

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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

R053BY008ND	Sandy
R053BY009ND	Shallow Loamy

R053BY008ND

Sandy

R053BY009ND

Shallow Loamy

Similar sites

R053BY008ND	Sandy [Does not receive additional moisture. Found on dry uplands upslope from Loamy Overflow sites, down slope from 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 has less sand bluestem, needleandthread and sedges, more blue grama, green needlegrass and western wheatgrass, slightly less production, similar landscape position.]
R053BY014ND	Choppy Sands [Deep entisol found on knobs and ridges of level to choppy sand blown plains; will not ribbon, found upslope from Sands sites; won’t ribbon. Indicator species: Sand bluestem, prairie sandreed and needleandthread evenly mixed, some Canada wildrye, penstemon, lemon scurfpea western ragweed, yucca, silky prairie clover and leadplant. This site has far less production, thin “A” horizon, no mollic epipedon, more needleandthread, choppier landscape.]

R053BY008ND

Sandy

[Does not receive additional moisture. Found on dry uplands upslope from Loamy Overflow sites, down slope from 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 has less sand bluestem, needleandthread and sedges, more blue grama, green needlegrass and western wheatgrass, slightly less production, similar landscape position.]

R053BY014ND

Choppy Sands

[Deep entisol found on knobs and ridges of level to choppy sand blown plains; will not ribbon, found upslope from Sands sites; won’t ribbon. Indicator species: Sand bluestem, prairie sandreed and needleandthread evenly mixed, some Canada wildrye, penstemon, lemon scurfpea western ragweed, yucca, silky prairie clover and leadplant. This site has far less production, thin “A” horizon, no mollic epipedon, more needleandthread, choppier landscape.]

Table 1. Dominant plant species

Tree	Not specified
Shrub	Not specified
Herbaceous	(1) Calamovilfa longifolia (2) Hesperostipa comata ssp. comata

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Physiographic features

This site typically occurs on nearly level to moderately steep uplands.

Table 2. Representative physiographic features

Landforms	(1) Dune (2) Till plain (3) Stream terrace
Flooding frequency	None
Ponding frequency	None
Elevation	1,600 – 2,000 ft
Slope	25%
Water table depth	80 in
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)	135 days
Freeze-free period (average)	156 days
Precipitation total (average)	20 in

Bar

Line

Figure 2. Monthly precipitation range

Bar

Line

Figure 3. Monthly average minimum and maximum temperature

Soil features

These are deep to very deep, well to excessively drained, coarse textured soils. Saturated hydraulic conductivity is rapid to very rapid and available water capacity is moderate to very low. Salinity and sodicity are none. Soils on this site are highly susceptible to wind erosion. This site is on nearly level to steep outwash plains, terraces and till plains. Slope ranges from 0 to 25 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. The soil surface is stable and intact.

These soils are susceptible to water and wind erosion. Loss of the soil surface layer can result in a shift in species composition and/or production.

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) Loamy fine sand (2) Loamy sand
Family particle size	(1) Sandy
Drainage class	Well drained to excessively drained
Permeability class	Rapid to very rapid
Soil depth	80 in
Surface fragment cover <=3"	15%
Surface fragment cover >3"	1%
Available water capacity (0-40in)	4 – 5 in
Calcium carbonate equivalent (0-40in)	15%
Electrical conductivity (0-40in)	2 mmhos/cm
Sodium adsorption ratio (0-40in)	Not specified
Soil reaction (1:1 water) (0-40in)	6.1 – 8.4
Subsurface fragment volume <=3" (Depth not specified)	15%
Subsurface fragment volume >3" (Depth not specified)	5%

Ecological dynamics

This 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 moderately resilient. Under continued adverse impacts, a slow decline in vegetative vigor and composition will occur. Under favorable vegetative management treatments the site can readily return to the Historic Climax Plant Community (HCPC).

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

Heavy continuous grazing or continuous seasonal grazing, without adequate recovery opportunities following each grazing event during the growing season, will initially cause needleandthread, blue grama and threadleaf sedge to increase. Species such as sand bluestem and prairie sandreed decrease in frequency and production. In time, heavy continuous grazing will likely cause blue grama and threadleaf sedge to dominate and other pioneer perennials and annuals to increase. In this case, runoff will increase and infiltration will decrease. Soil erosion will be minimal.

This site if heavily disturbed through improper grazing, wildfire, excessive defoliation or any type of physical disturbance can lead to serious erosion problems (blowout) on these fragile soils. 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. In time, shrubs such as yucca and cactus will likely become a major feature on this site.

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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State 1
Prairie Sandreed/Needleandthread/Bluestem

Community 1.1
Prairie Sandreed/Needleandthread/Bluestem

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 77% grasses or grass-like plants, 15% forbs, and 8% shrubs. The plant community is dominated by prairie sandreed, sand bluestem and needleandthread. Other grasses and grass-like plants occurring include little bluestem, blue grama, western wheatgrass, threadleaf and sun sedge. Significant forbs include penstemon, green sagewort, scurfpea and spiderwort. Leadplant, rose and fringed sagewort are the principal shrubs. 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. This is a sustainable plant community in terms of 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	1435	2125	2795
Forb	120	250	400
Shrub/Vine	45	125	205
Total	1600	2500	3400

Figure 5. Plant community growth curve (percent production by month). ND5304, Missouri Coteau, warm-season dominant, cool-season sub-dominant.. Warm-season dominant, cool-season sub-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	1	5	20	38	25	8	3	0	0	0

State 2
Needleandthread/Prairie Sandreed/Kentucky Bluegrass

Community 2.1
Needleandthread/Prairie Sandreed/Kentucky Bluegrass

This plant community develops after an extended period of 10 or more years of non-use by herbivores and exclusion of fire. A similar plant community may develop with heavy late seasonal grazing (every year at the same time of year), except the litter levels will not be as high. Non-native grasses, such as Kentucky bluegrass, crested wheatgrass, and smooth bromegrass tend to invade and may dominate this plant community. Other grasses present may include sand bluestem, prairie sandreed, little bluestem, western wheatgrass, and prairie junegrass. The common forbs include green sagewort, goldenrod, western wallflower, western ragweed and sweetclover. Fringed sagewort and prairie rose are the principal shrubs. Litter buildup reduces plant vigor and density, and native seedling recruitment declines. Due to a lack of tiller stimulation and sunlight, native bunchgrasses typically develop dead centers and native rhizomatous grasses are limited to small colonies. This plant community is 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. 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. Runoff is similar to the HCPC. Once this plant community is reached, time and external resources will be needed to see any immediate recovery in diversity.

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	1320	1936	2550
Shrub/Vine	40	132	225
Forb	40	132	225
Total	1400	2200	3000

Figure 7. Plant community growth curve (percent production by month). ND5302, Missouri Coteau, cool-season dominant, warm-season sub-dominant.. Cool-season dominant, warm-season sub-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	7	23	42	15	5	4	1	0	0

State 3
Needleandthread/Sedge/Dropseed/Forbs

Community 3.1
Needleandthread/Sedge/Dropseed/Forbs

This plant community is the result of long-term, heavy continuous grazing and/or heavy early seasonal grazing. Sand bluestem has been removed and prairie sandreed has been greatly reduced. Threadleaf sedge, blue grama and needleandthread have increased and are the dominant species. Other grasses include western wheatgrass, red threeawn, sand dropseed, and prairie junegrass. Forbs present include western ragweed, green sagewort, hairy goldaster, cudweed sagewort, scarlet globemallow and sweet clover. Fringed sagewort and cactus have also increased. Annual production, and consequently litter amounts, has been reduced substantially. Nutrient cycle, water cycle and energy flow are becoming impaired. This plant community is at risk of losing all tall warm season grasses. Wind scoured areas may exist where cover has been reduced or eliminated.

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	345	734	1320
Forb	40	112	185
Shrub/Vine	15	54	95
Total	400	900	1600

Figure 9. Plant community growth curve (percent production by month). ND5302, Missouri Coteau, cool-season dominant, warm-season sub-dominant.. Cool-season dominant, warm-season sub-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	7	23	42	15	5	4	1	0	0

State 4
Kentucky Bluegrass

Community 4.1
Kentucky Bluegrass

This plant community developed from continued heavy continuous season-long grazing without adequate recovery periods between grazing events or from continued non-use and no fire for extended periods of time. Kentucky bluegrass will tend to dominate this plant community; however, other non-native species such as smooth bromegrass and crested wheatgrass may also become prevalent. Sand bluestem and prairie sandreed are absent or nearly so, and other grasses and grass-likes present include sand dropseed, red threeawn, needleandthread, prairie junegrass and sun sedge. Forbs commonly found in this plant community include green sagewort, scurfpea, and sweetclover. When this plant community is reached through extended periods of non-use and no fire, litter buildup reduces native plant vigor and density severely, and native seedling recruitment is rare. Due to a lack of tiller stimulation and sunlight, native bunchgrasses typically develop dead centers and native rhizomatous grasses are limited to small colonies. This plant community can be dispersed throughout the pasture, encircling spot grazed areas, and areas distant from water sources. This is a sometimes found in properly stocked pastures grazed season-long.

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

Table 8. Annual production by plant type

Plant type	Low (lb/acre)	Representative value (lb/acre)	High (lb/acre)
Grass/Grasslike	895	1384	1865
Forb	75	160	250
Shrub/Vine	30	56	85
Total	1000	1600	2200

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 9. Community 1.1 plant community composition

Group	Common name	Symbol	Scientific name	Annual production (lb/acre)	Foliar cover (%)
Grass/Grasslike
1	Tall & Mid Warm-Season			500–925
	prairie sandreed	CALO	Calamovilfa longifolia	375–750	–
	sand bluestem	ANHA	Andropogon hallii	125–375	–
	little bluestem	SCSC	Schizachyrium scoparium	25–250	–
2	Needlegrass			125–375
	needle and thread	HECOC8	Hesperostipa comata ssp. comata	125–375	–
	porcupinegrass	HESP11	Hesperostipa spartea	25–125	–
3	Other Native Grasses			125–375
	blue grama	BOGR2	Bouteloua gracilis	50–125	–
	western wheatgrass	PASM	Pascopyrum smithii	0–125	–
	switchgrass	PAVI2	Panicum virgatum	0–125	–
	hairy grama	BOHI2	Bouteloua hirsuta	0–75	–
	Grass, perennial	2GP	Grass, perennial	25–75	–
	sand dropseed	SPCR	Sporobolus cryptandrus	0–50	–
	prairie Junegrass	KOMA	Koeleria macrantha	25–50	–
	Scribner's rosette grass	DIOLS	Dichanthelium oligosanthes var. scribnerianum	0–25	–
4	Grass-Likes			125–250
	threadleaf sedge	CAFI	Carex filifolia	75–175	–
	sun sedge	CAINH2	Carex inops ssp. heliophila	25–75	–
	Grass-like (not a true grass)	2GL	Grass-like (not a true grass)	25–50	–
Forb
6	Forbs			125–375
	tarragon	ARDR4	Artemisia dracunculus	25–100	–
	white sagebrush	ARLU	Artemisia ludoviciana	25–75	–
	Cuman ragweed	AMPS	Ambrosia psilostachya	25–75	–
	sunflower	HELIA3	Helianthus	25–75	–
	goldenrod	SOLID	Solidago	25–75	–
	hairy false goldenaster	HEVI4	Heterotheca villosa	25–50	–
	blazing star	LIATR	Liatris	0–50	–
	rush skeletonplant	LYJU	Lygodesmia juncea	25–50	–
	beardtongue	PENST	Penstemon	25–50	–
	scurfpea	PSORA2	Psoralidium	25–50	–
	upright prairie coneflower	RACO3	Ratibida columnifera	25–50	–
	yellow sundrops	CASE12	Calylophus serrulatus	25–50	–
	prairie clover	DALEA	Dalea	25–50	–
	blacksamson echinacea	ECAN2	Echinacea angustifolia	25–50	–
	sanddune wallflower	ERCAC	Erysimum capitatum var. capitatum	25–50	–
	wavyleaf thistle	CIUN	Cirsium undulatum	0–25	–
	Forb, perennial	2FP	Forb, perennial	0–25	–
	milkvetch	ASTRA	Astragalus	0–25	–
	large Indian breadroot	PEES	Pediomelum esculentum	0–25	–
	Nuttall's sensitive-briar	MINU6	Mimosa nuttallii	0–25	–
	longbract spiderwort	TRBR	Tradescantia bracteata	0–25	–
Shrub/Vine
7	Shrubs			50–200
	leadplant	AMCA6	Amorpha canescens	25–100	–
	western snowberry	SYOC	Symphoricarpos occidentalis	25–75	–
	rose	ROSA5	Rosa	25–50	–
	prairie sagewort	ARFR4	Artemisia frigida	25–50	–
	spinystar	ESVIV	Escobaria vivipara var. vivipara	0–25	–
	dwarf false indigo	AMNA	Amorpha nana	0–25	–
	Subshrub (<.5m)	2SUBS	Subshrub (<.5m)	0–25	–

Table 10. Community 2.1 plant community composition

Group	Common name	Symbol	Scientific name	Annual production (lb/acre)	Foliar cover (%)
Grass/Grasslike
1	Tall & Mid Warm-Season			220–440
	prairie sandreed	CALO	Calamovilfa longifolia	220–440	–
	little bluestem	SCSC	Schizachyrium scoparium	22–110	–
	sand bluestem	ANHA	Andropogon hallii	0–110	–
2	Needlegrass			220–440
	needle and thread	HECOC8	Hesperostipa comata ssp. comata	220–440	–
	porcupinegrass	HESP11	Hesperostipa spartea	0–66	–
3	Other Native Grasses			110–220
	Grass, perennial	2GP	Grass, perennial	0–110	–
	western wheatgrass	PASM	Pascopyrum smithii	0–110	–
	sand dropseed	SPCR	Sporobolus cryptandrus	22–110	–
	blue grama	BOGR2	Bouteloua gracilis	22–88	–
	Scribner's rosette grass	DIOLS	Dichanthelium oligosanthes var. scribnerianum	22–66	–
	prairie Junegrass	KOMA	Koeleria macrantha	22–66	–
	hairy grama	BOHI2	Bouteloua hirsuta	0–44	–
	switchgrass	PAVI2	Panicum virgatum	0–22	–
4	Grass-Likes			110–220
	threadleaf sedge	CAFI	Carex filifolia	66–220	–
	sun sedge	CAINH2	Carex inops ssp. heliophila	22–110	–
	Grass-like (not a true grass)	2GL	Grass-like (not a true grass)	0–66	–
5	Non-Native Grasses			110–440
	Kentucky bluegrass	POPR	Poa pratensis	110–330	–
	smooth brome	BRIN2	Bromus inermis	44–220	–
	cheatgrass	BRTE	Bromus tectorum	0–110	–
	crested wheatgrass	AGCR	Agropyron cristatum	0–110	–
Forb
6	Forbs			44–220
	Cuman ragweed	AMPS	Ambrosia psilostachya	22–110	–
	tarragon	ARDR4	Artemisia dracunculus	22–110	–
	white sagebrush	ARLU	Artemisia ludoviciana	22–110	–
	sunflower	HELIA3	Helianthus	22–110	–
	sweetclover	MELIL	Melilotus	0–110	–
	scurfpea	PSORA2	Psoralidium	22–66	–
	blazing star	LIATR	Liatris	22–66	–
	Forb, annual	2FA	Forb, annual	0–66	–
	Forb, perennial	2FP	Forb, perennial	0–66	–
	goldenrod	SOLID	Solidago	22–66	–
	sanddune wallflower	ERCAC	Erysimum capitatum var. capitatum	0–44	–
	prairie clover	DALEA	Dalea	22–44	–
	upright prairie coneflower	RACO3	Ratibida columnifera	22–44	–
	beardtongue	PENST	Penstemon	0–22	–
	rush skeletonplant	LYJU	Lygodesmia juncea	0–22	–
	hairy false goldenaster	HEVI4	Heterotheca villosa	0–22	–
	blacksamson echinacea	ECAN2	Echinacea angustifolia	0–22	–
	milkvetch	ASTRA	Astragalus	0–22	–
	yellow sundrops	CASE12	Calylophus serrulatus	0–22	–
	wavyleaf thistle	CIUN	Cirsium undulatum	0–22	–
Shrub/Vine
7	Shrubs			44–220
	prairie sagewort	ARFR4	Artemisia frigida	22–110	–
	rose	ROSA5	Rosa	22–110	–
	western snowberry	SYOC	Symphoricarpos occidentalis	22–88	–
	Subshrub (<.5m)	2SUBS	Subshrub (<.5m)	0–44	–
	leadplant	AMCA6	Amorpha canescens	0–22	–
	spinystar	ESVIV	Escobaria vivipara var. vivipara	0–22	–

Table 11. Community 3.1 plant community composition

Group	Common name	Symbol	Scientific name	Annual production (lb/acre)	Foliar cover (%)
Grass/Grasslike
1	Tall & Mid Warm-Season			0–45
	prairie sandreed	CALO	Calamovilfa longifolia	0–45	–
	little bluestem	SCSC	Schizachyrium scoparium	0–27	–
2	Needlegrass			45–225
	needle and thread	HECOC8	Hesperostipa comata ssp. comata	45–225	–
3	Other Native Grasses			45–180
	sand dropseed	SPCR	Sporobolus cryptandrus	18–135	–
	Grass, perennial	2GP	Grass, perennial	0–45	–
	blue grama	BOGR2	Bouteloua gracilis	9–45	–
	hairy grama	BOHI2	Bouteloua hirsuta	0–45	–
	Scribner's rosette grass	DIOLS	Dichanthelium oligosanthes var. scribnerianum	9–45	–
	western wheatgrass	PASM	Pascopyrum smithii	0–27	–
	prairie Junegrass	KOMA	Koeleria macrantha	0–18	–
4	Grass-Likes			45–135
	threadleaf sedge	CAFI	Carex filifolia	45–135	–
	sun sedge	CAINH2	Carex inops ssp. heliophila	9–63	–
	Grass-like (not a true grass)	2GL	Grass-like (not a true grass)	0–45	–
5	Non-Native Grasses			0–45
	Kentucky bluegrass	POPR	Poa pratensis	0–45	–
	smooth brome	BRIN2	Bromus inermis	0–27	–
	cheatgrass	BRTE	Bromus tectorum	0–27	–
Forb
6	Forbs			45–180
	sweetclover	MELIL	Melilotus	0–90	–
	tarragon	ARDR4	Artemisia dracunculus	18–90	–
	sunflower	HELIA3	Helianthus	9–72	–
	Cuman ragweed	AMPS	Ambrosia psilostachya	18–72	–
	white sagebrush	ARLU	Artemisia ludoviciana	9–45	–
	Forb, annual	2FA	Forb, annual	0–45	–
	Forb, perennial	2FP	Forb, perennial	0–45	–
	goldenrod	SOLID	Solidago	9–36	–
	scurfpea	PSORA2	Psoralidium	9–36	–
	blazing star	LIATR	Liatris	9–27	–
	prairie clover	DALEA	Dalea	0–18	–
	sanddune wallflower	ERCAC	Erysimum capitatum var. capitatum	0–18	–
	upright prairie coneflower	RACO3	Ratibida columnifera	9–18	–
	rush skeletonplant	LYJU	Lygodesmia juncea	0–9	–
	wavyleaf thistle	CIUN	Cirsium undulatum	0–9	–
Shrub/Vine
7	Shrubs			18–90
	prairie sagewort	ARFR4	Artemisia frigida	18–90	–
	rose	ROSA5	Rosa	9–72	–
	western snowberry	SYOC	Symphoricarpos occidentalis	9–36	–
	Subshrub (<.5m)	2SUBS	Subshrub (<.5m)	0–18	–
	spinystar	ESVIV	Escobaria vivipara var. vivipara	0–9	–

Table 12. Community 4.1 plant community composition

Group	Common name	Symbol	Scientific name	Annual production (lb/acre)	Foliar cover (%)
Grass/Grasslike
1	Tall & Mid Warm-Season			0–32
	prairie sandreed	CALO	Calamovilfa longifolia	0–32	–
	little bluestem	SCSC	Schizachyrium scoparium	0–16	–
2	Needlegrass			16–128
	needle and thread	HECOC8	Hesperostipa comata ssp. comata	16–128	–
3	Other Native Grasses			32–160
	western wheatgrass	PASM	Pascopyrum smithii	0–80	–
	sand dropseed	SPCR	Sporobolus cryptandrus	16–80	–
	Scribner's rosette grass	DIOLS	Dichanthelium oligosanthes var. scribnerianum	0–48	–
	prairie Junegrass	KOMA	Koeleria macrantha	16–48	–
	Grass, perennial	2GP	Grass, perennial	0–48	–
	blue grama	BOGR2	Bouteloua gracilis	0–48	–
	hairy grama	BOHI2	Bouteloua hirsuta	0–32	–
4	Grass-Likes			0–80
	threadleaf sedge	CAFI	Carex filifolia	0–80	–
	sun sedge	CAINH2	Carex inops ssp. heliophila	0–48	–
	Grass-like (not a true grass)	2GL	Grass-like (not a true grass)	0–32	–
5	Non-Native Grasses			480–880
	Kentucky bluegrass	POPR	Poa pratensis	240–720	–
	smooth brome	BRIN2	Bromus inermis	80–480	–
	cheatgrass	BRTE	Bromus tectorum	0–160	–
	crested wheatgrass	AGCR	Agropyron cristatum	0–160	–
7	Shrubs			32–80
	prairie sagewort	ARFR4	Artemisia frigida	16–80	–
	rose	ROSA5	Rosa	16–48	–
	western snowberry	SYOC	Symphoricarpos occidentalis	0–32	–
	Subshrub (<.5m)	2SUBS	Subshrub (<.5m)	0–32	–
Forb
6	Forbs			80–240
	sweetclover	MELIL	Melilotus	0–160	–
	Forb, annual	2FA	Forb, annual	0–80	–
	Forb, perennial	2FP	Forb, perennial	0–80	–
	Cuman ragweed	AMPS	Ambrosia psilostachya	16–80	–
	tarragon	ARDR4	Artemisia dracunculus	16–80	–
	white sagebrush	ARLU	Artemisia ludoviciana	16–80	–
	sunflower	HELIA3	Helianthus	16–80	–
	scurfpea	PSORA2	Psoralidium	16–48	–
	goldenrod	SOLID	Solidago	16–48	–
	sanddune wallflower	ERCAC	Erysimum capitatum var. capitatum	0–32	–
	upright prairie coneflower	RACO3	Ratibida columnifera	16–32	–
	blazing star	LIATR	Liatris	16–32	–
	prairie clover	DALEA	Dalea	0–32	–
	blacksamson echinacea	ECAN2	Echinacea angustifolia	0–16	–
	milkvetch	ASTRA	Astragalus	0–16	–
	wavyleaf thistle	CIUN	Cirsium undulatum	0–16	–

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 groups A and B. Infiltration varies from very rapid to rapid and runoff potential varies from negligible to low 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.

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	01/17/2012
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):
10 to 15%.
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):
Soil aggregate stability ratings should typically be greater than 5. 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):
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:
Mid and tall warm-season grasses >

Sub-dominant:
Mid, cool-season grasses > forbs

Other:
Grass-likes > short, warm-season grasses > shrubs > short cool-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):
None.
Average percent litter cover (%) and depth ( in):
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
Representaive value = 2500 lbs/ac air dry with a range of 1600 to 3400 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 R053BY007ND

Sands

Last updated: 1/11/2024 Accessed: 12/21/2024

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

State 4 submodel, plant communities

Natural Resources
Conservation Service

Last updated: 1/11/2024
Accessed: 12/21/2024