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Ecological site R010XY009OR

Sandy Bottom

Last updated: 12/13/2023
Accessed: 12/22/2024

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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.

MLRA notes

Major Land Resource Area (MLRA): 010X–Central Rocky and Blue Mountain Foothills

This MLRA is characterized by gently rolling to steep hills, plateaus, and low mountains at the foothills of the Blue Mountains in Oregon and the Central Rocky Mountains in Idaho. The geology of this area is highly varied and ranges from Holocene volcanics to Cretaceous sedimentary rocks. Mollisols are the dominant soil order and the soil climate is typified by mesic or frigid soil temperature regimes, and xeric or aridic soil moisture regimes. Elevation ranges from 1,300 to 6,600 feet (395 to 2,010 meters), increasing from west to east. The climate is characterized by dry summers and snow dominated winters with precipitation averaging 8 to 16 inches (205 to 405 millimeters) and increasing from west to east. These factors support plant communities with shrub-grass associations with considerable acreage of sagebrush grassland. Big sagebrush, bluebunch wheatgrass, and Idaho fescue are the dominant species. Stiff sagebrush, low sagebrush, and Sandberg bluegrass are often dominant on sites with shallow restrictive layers. Western juniper is one of the few common tree species and since European settlement has greatly expanded its extent in Oregon. Nearly half of the MLRA is federally owned and managed by the Bureau of Land Management. Most of the area is used for livestock grazing with areas accessible by irrigation often used for irrigated agriculture.

Ecological site concept

In reference condition, this site supports a highly productive bottomland plant community dominated by is dominated by great basin wildrye (Leymus cinereus) with needle and thread (Hesperostipa comata) and basin big sagebrush (Artemisia tridentata ssp. tridentata) also common. Abiotically, this site is characterized by nearly level slopes on floodplains or swales with typically deep alluvial soils. The soil temperature regime of this site is mesic. Historically, the ecological dynamics of this site were driven by fire and drought. Presently, reference conditions are less common and current dynamics are also influenced by the spread of invasive species, livestock grazing pressures and fire suppression.

This is a provisional ecological site whose accelerated development from a draft site was undertaken with little to no field verification and is subject to extensive review and revision before final approval. All data herein was developed using existing information and literature and should be considered provisional and contingent upon field validation prior to use in conservation planning.

Associated sites

R010XY010OR	Coyote Willow Riparian Adjacent riparian areas dominated by narrowleaf willow
R010XY005OR	Loamy Bottom Adjacent bottomlands with loamy soils

R010XY010OR

Coyote Willow Riparian

Adjacent riparian areas dominated by narrowleaf willow

R010XY005OR

Loamy Bottom

Adjacent bottomlands with loamy soils

Similar sites

R010XY007OR	Sodic Bottom Soils are sodic
R010XY014OR	Clayey Bottom Soils are clayey
R010XY005OR	Loamy Bottom Soils are loamy

R010XY007OR

Sodic Bottom

Soils are sodic

R010XY014OR

Clayey Bottom

Soils are clayey

R010XY005OR

Loamy Bottom

Soils are loamy

Table 1. Dominant plant species

Tree	Not specified
Shrub	Not specified
Herbaceous	(1) Leymus cinereus (2) Hesperostipa comata

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Physiographic features

This site occurs on nearly level to gently sloping floodplains, terraces and swales. Slopes range from 0 to 10 percent. Elevation varies from 1,400 to 2,400 feet (425 to 650 meters). A water table from 48 to 72 inches (120 to 180 cm) below the surface may occur during winter and spring months.

Table 2. Representative physiographic features

Landforms	(1) Valley > Flood plain (2) Valley > Swale (3) Valley > Terrace
Flooding duration	Extremely brief (0.1 to 4 hours) to brief (2 to 7 days)
Flooding frequency	Very rare to occasional
Ponding frequency	None
Elevation	427 – 732 m
Slope	0 – 10%
Water table depth	122 – 183 cm
Aspect	Aspect is not a significant factor

Climatic features

This site receives 9 to 12 inches (225 to 300mm) of mean annual precipitation primarily as rain November through April. This site has a mesic soil temperature regime and a frost-free period of approximately 100 to 180 days. Climate graphs are based on the nearest available climate stations to representative site locations and are provided to indicate general climate patterns.

Table 3. Representative climatic features

Frost-free period (characteristic range)	100-180 days
Freeze-free period (characteristic range)
Precipitation total (characteristic range)	229-305 mm
Frost-free period (average)	140 days
Freeze-free period (average)
Precipitation total (average)	279 mm

Characteristic range

Actual range

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Figure 1. Monthly precipitation range

Characteristic range

Actual range

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Figure 2. Monthly minimum temperature range

Characteristic range

Actual range

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Figure 3. Monthly maximum temperature range

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Figure 4. Monthly average minimum and maximum temperature

Figure 5. Annual precipitation pattern

Figure 6. Annual average temperature pattern

Climate stations used

(1) MONUMENT 2 [USC00355711], Monument, OR
(2) JOHN DAY 35 WNW [USW00004125], Mitchell, OR
(3) MITCHELL 2 NW [USC00355641], Mitchell, OR

Influencing water features

The water table of this site is influenced by the adjacent stream course which will vary depending on the contributing area as well as the biotic and hydrologic integrity of the surrounding watershed.

Wetland description

Not applicable

Soil features

Typically a deep to very deep fine sandy to sandy loam derived from alluvium. Family particle size is typically coarse loamy or coarse-loamy over sandy or sandy-skeletal. See Kimberly for a typical soil correlated to this site.

Table 4. Representative soil features

Parent material	(1) Alluvium – volcanic and sedimentary rock
Surface texture	(1) Sandy loam (2) Fine sandy loam
Family particle size	(1) Coarse-loamy over sandy or sandy-skeletal (2) Coarse-loamy
Drainage class	Moderately well drained to somewhat excessively drained
Permeability class	Moderately slow to rapid
Depth to restrictive layer	102 – 203 cm
Soil depth	102 – 203 cm
Surface fragment cover <=3"	0 – 15%
Surface fragment cover >3"	0 – 15%
Available water capacity (0-101.6cm)	7.62 – 15.24 cm
Soil reaction (1:1 water) (0-101.6cm)	6.6 – 8.4
Subsurface fragment volume <=3" (10.2-152.4cm)	0 – 45%
Subsurface fragment volume >3" (10.2-152.4cm)	0 – 15%

Ecological dynamics

The reference plant community is characterized by basin wildrye (LECI4), needle and thread (HECO26), and basin big sagebrush (ARTRT). Basin wildrye increases with seasonal availability of subsurface lateral water flows. Needleandthread increases on drier sites with limited subsurface flows. Basin big sagebrush increases in the absence of fire. This is a highly productive site with average production varying between 2000 and 5000 pounds per acre.

Overgrazing causes a decrease in basin wildrye and an increase in basin big sagebrush along with an increase in creeping wildrye, greasewood and rabbitbrush if present. Continued deterioration of these sites promotes shrub dominance, increased bare ground and the invasion of annual weeds, primarily cheatgrass. On sites with salt affected soils, surface conditions become increasingly sodic. Long-term abusive grazing may eliminate understory grasses and promote a decadent sagebrush stand with a cheatgrass understory (Stringham, 2009).

State and transition model

More interactive model formats are also available. View Interactive Models
Click on state and transition labels to scroll to the respective text

Ecosystem states

1. Historical Reference State

2. Current Potential

3. Shrub Dominant

4. Annual Grass Dominant

T1A	-	Introduction of invasive plant species
T2A	-	Prolonged, improperly managed grazing, possibly in combination with a long interval in the absence of fire.
R3A	-	Requires mechanical or herbicide treatment of brush species and control of invasive weeds. Fire is not recommended. If basin wildrye is not apparent, seeding may be required.
T3A	-	Further prolonged improperly managed grazing, fire
R4A	-	Requires control of invasive weeds. Fire is not recommended . If basin wildrye is not apparent, seeding will likely be required.

State 1 submodel, plant communities

1.1. Reference Plant Community

1.2. Shrubs/Perennial Grasses

1.3. Basin Wildrye/Rabbitbrush

1.1A	-	Chronic Drought or abusive grazing practices
1.1B	-	Chronic Drought or abusive grazing practices
1.2A	-	Low intensity fire combined with prescribed grazing
1.2B	-	Low intensity fire combined with prescribed grazing
1.3A	-	Low intensity fire combined with prescribed grazing

State 2 submodel, plant communities

2.1. Perennial Grasses/Sagebrush/Annuals

2.2. Shrubs/ Perennial Grasses/Annuals

2.3. Basin Wildrye/Rabbitbrush/Annuals

2.1A	-	Chronic drought or abusive grazing practices
2.2A	-	Low intensity fire combined with prescribed grazing
2.3A	-	Low intensity fire combined with prescribed grazing

State 3 submodel, plant communities

3.1. Shrub/Cheatgrass

State 4 submodel, plant communities

4.1. Cheatgrass

State 1
Historical Reference State

Community phase changes are a function of fire and/or chronic drought. The existence of the reference state today is rare. Fire played a significant role in the community phase dynamics of the reference state; however, the time between fires would be highly variable and dependent upon the location and productivity of the site. Chronic drought leads to a reduction in native grasses and an increase in sagebrush or greasewood dominance while low-intensity fire maintains state dynamics.

Dominant plant species

basin wildrye (Leymus cinereus), grass
needle and thread (Hesperostipa comata ssp. comata), grass

Community 1.1
Reference Plant Community

Dominated by herbaceous vegetation, primarily basin wildrye, needle and thread, and thickspike wheatgrass. Scattered basin big sagebrush.

Dominant plant species

basin wildrye (Leymus cinereus), grass

Figure 7. 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	2130	3194	5335
Shrub/Vine	112	168	269
Forb	–	–	–
Total	2242	3362	5604

Community 1.2
Shrubs/Perennial Grasses

Sagebrush and other shrubs increase; grass production declines; rabbitbrush may increase, bare ground increases.

Community 1.3
Basin Wildrye/Rabbitbrush

Sagebrush and other shrubs decline; basin wildrye increases; rabbitbrush may increase.

Pathway 1.1A
Community 1.1 to 1.2

Chronic Drought or abusive grazing practices

Pathway 1.1B
Community 1.1 to 1.3

Chronic Drought or abusive grazing practices

Pathway 1.2A
Community 1.2 to 1.1

Low intensity fire combined with prescribed grazing

Pathway 1.2B
Community 1.2 to 1.3

Low intensity fire combined with prescribed grazing

Pathway 1.3A
Community 1.3 to 1.1

Low intensity fire combined with prescribed grazing

State 2
Current Potential

Compositionally similar to the reference state with the addition of a trace of annual weeds, primarily cheatgrass. Ecological function has not changed, however the resiliency of the state has been reduced by the presence of invasive weeds. Abusive grazing practices and or chronic drought leads to a reduction in native grasses and an increase in sagebrush or greasewood dominance creating an at-risk community phase (CP1). Low-intensity fire combined with prescribed grazing maintains state dynamics (CP2 & CP3).

Dominant plant species

basin wildrye (Leymus cinereus), grass
needle and thread (Hesperostipa comata ssp. comata), grass

Community 2.1
Perennial Grasses/Sagebrush/Annuals

Dominated by herbaceous vegetation, primarily basin wildrye, needle and thread, and thickspike wheatgrass. Scattered basin big sagebrush; cheatgrass or other annual weeds present in trace amounts.

Community 2.2
Shrubs/ Perennial Grasses/Annuals

Sagebrush and other shrubs increase; grass production declines; rabbitbrush may increase; bare ground increases; cheatgrass or other annuals increase (At Risk Phase).

Community 2.3
Basin Wildrye/Rabbitbrush/Annuals

Sagebrush and other shrubs decline; basin wildrye increases; rabbitbrush may increase; cheatgrass present.

Pathway 2.1A
Community 2.1 to 2.2

Chronic drought or abusive grazing practices

Pathway 2.2A
Community 2.2 to 2.3

Low intensity fire combined with prescribed grazing

Pathway 2.3A
Community 2.3 to 2.1

Low intensity fire combined with prescribed grazing

State 3
Shrub Dominant

Decadent sagebrush dominates the overstory and cheatgrass dominates the understory. A significant reduction/loss of basin wildrye and other grasses is apparent. Bare ground is abundant. Spatial and temporal energy capture and nutrient cycling has been truncated. Infiltration may be reduced due to lack of ground cover.

Dominant plant species

basin big sagebrush (Artemisia tridentata ssp. tridentata), shrub
greasewood (Sarcobatus vermiculatus), shrub
rabbitbrush (Chrysothamnus), shrub
broom snakeweed (Gutierrezia sarothrae), shrub

Community 3.1
Shrub/Cheatgrass

Decadent sagebrush is dominant; greasewood and rabbitbrush may be significant overstory components; cheatgrass dominates the understory; basin wildrye and other perennial grasses are trace; bare ground increases.

State 4
Annual Grass Dominant

The site has crossed an abiotic threshold and ecological dynamics are determined by frequent fire, cheatgrass dominance, lack of shrubby plants, bare ground, soil movement by wind and water erosion.

Dominant plant species

cheatgrass (Bromus tectorum), grass
medusahead (Taeniatherum caput-medusae), grass

Community 4.1
Cheatgrass

Cheatgrass and other annuals dominant; bare ground prominent.

Transition T1A
State 1 to 2

Introduction of invasive plant species

Transition T2A
State 2 to 3

Prolonged, improperly managed grazing, possibly in combination with a long interval in the absence of fire.

Constraints to recovery. Irreversible transition has occurred and a biotic threshold has been crossed. Brush species and cheatgrass control site dynamics.

Restoration pathway R3A
State 3 to 2

Requires mechanical or herbicide treatment of brush species and control of invasive weeds. Fire is not recommended. If basin wildrye is not apparent, seeding may be required.

Transition T3A
State 3 to 4

Further prolonged improperly managed grazing, fire

Constraints to recovery. Irreversible transition has occurred and an abiotic threshold has been crossed. Frequent fire promotes maintenance of cheatgrass dominance. Wind and water erosion of soil increases and may become a dominant ecological process driving site dynamics.

Restoration pathway R4A
State 4 to 2

Requires control of invasive weeds. Fire is not recommended . If basin wildrye is not apparent, seeding will likely be required.

Additional community tables

Table 6. Community 1.1 plant community composition

Group	Common name	Symbol	Scientific name	Annual production (kg/hectare)	Foliar cover (%)
Grass/Grasslike
1	Perennial Grasses			2354–3363
	basin wildrye	LECI4	Leymus cinereus	2018–2522	–
	needle and thread	HECO26	Hesperostipa comata	168–504	–
	thickspike wheatgrass	ELLAL	Elymus lanceolatus ssp. lanceolatus	168–336	–
2	Other Perennial Grasses			–
	Sandberg bluegrass	POSE	Poa secunda	–	–
	bluebunch wheatgrass	PSSPS	Pseudoroegneria spicata ssp. spicata	–	–
	sand dropseed	SPCR	Sporobolus cryptandrus	–	–
	Indian ricegrass	ACHY	Achnatherum hymenoides	–	–
	squirreltail	ELEL5	Elymus elymoides	–	–
3	Big Bluegrass			101–168
	Sandberg bluegrass	POSE	Poa secunda	101–168	–
Forb
4	Forbs			–
	milkvetch	ASTRA	Astragalus	–	–
	common yarrow	ACMI2	Achillea millefolium	–	–
	lupine	LUPIN	Lupinus	–	–
	buckwheat	ERIOG	Eriogonum	–	–
	desertparsley	LOMAT	Lomatium	–	–
	phlox	PHLOX	Phlox	–	–
Shrub/Vine
7	Shrubs			67–235
	basin big sagebrush	ARTRT	Artemisia tridentata ssp. tridentata	67–168	–
	broom snakeweed	GUSA2	Gutierrezia sarothrae	0–67	–
8	Other Shrubs			–
	rabbitbrush	CHRYS9	Chrysothamnus	–	–
	greasewood	SAVE4	Sarcobatus vermiculatus	–	–

Supporting information

References

. Fire Effects Information System. http://www.fs.fed.us/database/feis/.
. 2021 (Date accessed). USDA PLANTS Database. http://plants.usda.gov.

Other references

Stringham, T.K. 2009. Final Report for Agreement No. 68-0436-8-040 USDA Ecological Site Description MLRA D23 & D24. University of Nevada, Reno.

Contributors

Jenni Moffitt, general updates 2020
Ed Petersen, Alan Bahn, original authors
2021 updates Andrew Neary

Approval

Kirt Walstad, 12/13/2023

Rangeland health reference sheet

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

Author(s)/participant(s)
Contact for lead author
Date	08/07/2012
Approved by	Kirt Walstad
Approval date
Composition (Indicators 10 and 12) based on	Annual Production