Ecological site R024XY033OR

R024XY030OR	LOAMY SLOPES 6-10 PZ Loamy Slopes 6-10 PZ (lower production, warmer slope, different composition – ARTRW8 and ACHY dominant w/ACTH7 prominent, PSSPS and GRSP present)
R024XY015OR	DESERT LOAM 6-10 PZ Desert Loam 6-10 PZ (non-aspect, lower production, different composition – ATCO and PIDE4 dominant)
R024XY016OR	LOAMY 8-10 PZ Loamy 8-10 PZ (non-aspect, different composition – ACTH7 dominant, PSSPS prominent)
R024XY017OR	SHALLOW LOAM 8-10 PZ Shallow Loam 8-10 PZ (non-aspect, lower production, different composition – ACTH7 dominant, ACHY and PSSPS prominent)
R024XY020OR	SHRUBBY LOAM 8-10 PZ Shrubby Loam 8-10 PZ (non-aspect, different composition - EPHED present, ACTH7 dominant, PSSPS prominent)
R024XY031OR	DROUGHTY SHALLOW SLOPES 6-10 PZ Droughty Shallow Slopes 6-10 PZ (lower production, warmer slope, higher soluble salts, different composition – ATCO and PIDE4 dominant, ACHY and ELEL5 prominent)
R024XY032OR	ARID SOUTH SLOPES 6-10 PZ Arid South Slopes 6-10 PZ (lower production, warmer slope, different composition – ARTRW8 and ACHY dominant w/ACTH7 prominent, PSSPS and SADO4 present)
R024XY602OR	NORTH SLOPES 8-10 PZ North Slopes 8-10 PZ (moderate deep, cobbly ashy loam surface, higher production, cooler slopes, different composition – ARTRW8 and PSSPS dominant w/ACTH7 and POCU3 prominent)
R024XY638OR	SOUTH SLOPES 8-10 PZ South Slopes 8-10 PZ (higher production, warmer slope, different composition – ARTRW8 and PSSPS dominant w/ACTH7 near co-dominant)

R024XY638OR	SOUTH SLOPES 8-10 PZ South Slopes 8-10 PZ (higher production, warmer slope, different composition – ARTRW8 and PSSPS dominant w/ACTH7 near co-dominant)
R024XY602OR	NORTH SLOPES 8-10 PZ North Slopes 8-10 PZ (moderate deep, cobbly ashy loam surface, higher production, cooler slopes, different composition – ARTRW8 and PSSPS dominant w/ACTH7 and POCU3 prominent)

Tree	Not specified
Shrub	(1) Artemisia tridentata ssp. wyomingensis
Herbaceous	(1) Pseudoroegneria spicata ssp. spicata (2) Achnatherum thurberianum

Landforms	(1) Terrace (2) Hill (3) Mountain slope
Elevation	3500 – 5200 ft
Slope	20 – 70 %
Aspect	N

Frost-free period (average)	110 days
Freeze-free period (average)	0 days
Precipitation total (average)	10 in

Parent material	(1) Volcanic ash – rhyolite
Surface texture	(1) Very cobbly sandy clay loam (2) Extremely stony silty clay loam (3) Very gravelly sandy loam
Family particle size	(1) Clayey
Drainage class	Moderately well drained to somewhat poorly drained
Permeability class	Moderately slow to slow
Soil depth	8 – 20 in
Available water capacity (0-40in)	2 – 4 in

Ecological dynamics

The reference native plant community is dominated by Wyoming big sagebrush and bluebunch wheatgrass. Thurber's needlegrass is prominent. Spiny hopsage, Indian ricegrass, bottlebrush squirreltail and Sandberg bluegrass are present. Mormon tea is sporadic. Vegetative composition of the community is approximately 70 percent grasses, 10 percent forbs and 20 percent shrubs. The approximate ground cover is 40 to 50 percent (basal and crown).

Four states have been identified for this site: a reference state; a state with the presence of annuals; a state with a shrub/annual co-dominance; and a state with annual dominance.

Reference: Plant community phase change is driven by infrequent fire. Wyoming and basin big sagebrush decline after fire while Thurber’s needlegrass, Indian ricegrass and other grasses increase. May see a temporary increase in rabbitbrush after fire. Time facilitates the reintroduction of sagebrush. The introduction of invasive annual grasses and forbs transitions into the state 2.

State 2: Compositionally similar to the reference state with a trace of cheatgrass and weedy forbs. Ecological function has not changed, however the resiliency of the state has been reduced by the presence of invasive weeds. Prescribed grazing and infrequent fire (> 50 year return interval) maintain state dynamics. The timing and/or intensity of grazing or prolonged drought favors Wyoming and basin big sagebrush, squirreltail and Sandberg’s bluegrass. Prescribed grazing and/or release from drought may reverse the decline in needlegrass and Indian ricegrass production. Infrequent fire reduces the shrub community and promotes the bunchgrass component. Mismanaged grazing and/or prolonged drought leads to a biotic threshold and into state 3.

State 3: Wyoming and basin big sagebrush is decadent with little recruitment. The perennial grass component is significantly reduced in both density and productivity. Cheatgrass and/or annual forbs and/or Sandberg’s bluegrass along with sagebrush control site resources and drive ecological dynamics. 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. Risk of soil erosion by both wind and water is increased. Catastrophic wildfire will lead to an abiotic threshold and into state 4.

State 4: Cheatgrass and/or annual weed dominated plant community with limited to no shrub or perennial grass component. Soil erosion and redistribution along with changes in dynamic soil properties affect the hydrologic cycle and thus the nutrient cycle. Harsh environmental factors increase state resiliency to change.

Range in Characteristics
The depth to a restrictive layer and aspect influences the composition and production of the site. Production will increase with greater soil depth and at the upper end of the precipitation zone. Bluebunch wheatgrass increases on a silty surface. Thurber’s needlegrass increases on shallow coarser soils. Spiny hopsage increases at the lower end of the precipitation zone and on droughty slopes. Mormon tea occurs sporadically increasing on toe slopes and over highly fractured substrata. On older stable higher terraces an erosion pavement has accumulated with a distinctive desert varnish. The distinctive dark color is due to precipitated concentrates of manganese and lesser amounts of iron.

Response to Disturbance - States
If the condition of the site deteriorates as a result of over grazing, bluebunch wheatgrass and Thurber needlegrass will decrease in the stand. Wyoming big sagebrush, squirreltail and Sandberg bluegrass will increase. Minor amounts of annuals will invade. With further deterioration, bare ground rapidly increases, erosion accelerates and site productivity decreases. The invasion of annuals and the natural re-establishment of native perennials are limited on eroded surfaces and in areas of dense cobbles and heavy erosion pavement.

States: ARTRW8-GRSP/ELEL5-POSE-bare ground with erosion pavement; Annuals (scattered)-bare ground with erosion pavement

State and transition model

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Standard diagram

Figure 4. Group 6, STM

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Click on state and transition labels to scroll to the respective text

Ecosystem states

1. Reference State

State 1 submodel, plant communities

1.1. Reference Plant Community

State 1
Reference State

Community 1.1
Reference Plant Community

Figure 5. 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	280	420	560
Shrub/Vine	80	120	160
Forb	40	60	80
Total	400	600	800

Additional community tables

Table 6. Community 1.1 plant community composition

Group	Common name	Symbol	Scientific name	Annual production ()	Foliar cover (%)
Grass/Grasslike
1	Dominant, moderate rooted bunchgrass			240–300
	bluebunch wheatgrass	PSSPS	Pseudoroegneria spicata ssp. spicata	240–300	–
2	Sub-dominant, moderate rooted bunchgrass			120–240
	Thurber's needlegrass	ACTH7	Achnatherum thurberianum	120–240	–
3	Other Perennial Grasses			50–120
	Indian ricegrass	ACHY	Achnatherum hymenoides	12–30	–
	squirreltail	ELEL5	Elymus elymoides	0–12	–
	basin wildrye	LECI4	Leymus cinereus	0–12	–
	Sandberg bluegrass	POSE	Poa secunda	0–12	–
	foxtail wheatgrass	PSSA2	×Pseudelymus saxicola	0–12	–
Forb
4	Perennial forbs			12–60
	common yarrow	ACMI2	Achillea millefolium	0–12	–
	pussytoes	ANTEN	Antennaria	0–12	–
	rockcress	ARABI	Arabidopsis	0–12	–
	milkvetch	ASTRA	Astragalus	0–12	–
	arrowleaf balsamroot	BASA3	Balsamorhiza sagittata	0–12	–
	mariposa lily	CALOC	Calochortus	0–12	–
	Indian paintbrush	CASTI2	Castilleja	0–12	–
	tapertip hawksbeard	CRAC2	Crepis acuminata	0–12	–
	fleabane	ERIGE2	Erigeron	0–12	–
	buckwheat	ERIOG	Eriogonum	0–12	–
	lupine	LUPIN	Lupinus	0–12	–
	spreading phlox	PHDI3	Phlox diffusa	0–12	–
	deathcamas	ZIGAD	Zigadenus	0–12	–
Shrub/Vine
5	Evergreen Shrub			60–90
	Wyoming big sagebrush	ARTRW8	Artemisia tridentata ssp. wyomingensis	60–90	–
6	Other shrubs			24–66
	mormon tea	EPVI	Ephedra viridis	0–60	–
	spiny hopsage	GRSP	Grayia spinosa	12–30	–
	littleleaf horsebrush	TEGL	Tetradymia glabrata	0–12	–
	yellow rabbitbrush	CHVI8	Chrysothamnus viscidiflorus	0–12	–

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
Approved by
Approval date
Composition (Indicators 10 and 12) based on	Annual Production

Indicators

Number and extent of rills:
Presence of water flow patterns:
Number and height of erosional pedestals or terracettes:
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
Number of gullies and erosion associated with gullies:
Extent of wind scoured, blowouts and/or depositional areas:
Amount of litter movement (describe size and distance expected to travel):
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on 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:

Sub-dominant:

Other:

Additional:
Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
Average percent litter cover (%) and depth ( in):
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
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:
Perennial plant reproductive capability:

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Ecological site R024XY033OR

ARID NORTH SLOPES 6-10 PZ

Accessed: 04/14/2026

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General information

Figure 1. Mapped extent

Associated sites

Similar sites

Table 1. Dominant plant species

Natural Resources
Conservation Service

ARID NORTH SLOPES
6-10 PZ