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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.
Associated sites
R021XY210OR LOAMY 14-18 PZ
R021XY214OR CLAYPAN 14-18 PZ
R021XY308OR SOUTH SLOPES 14-18 PZ
R021XY310OR SHALLOW NORTH 14-18 PZ
R021XY312OR NORTH SLOPES 14-18 PZ
Table 1. Dominant plant species
Tree Not specified
Shrub Not specified
Herbaceous Not specified
Physiographic features
This site occurs on all aspects of mountain ridges and sideslopes. Slopes range form 0 to 70%. Elevations range from 4200 to 6000 feet.
Table 2. Representative physiographic features
Landforms (1) Mountain slope
(2) Ridge
Elevation 4200 – 6000 ft Slope 0 – 70 % Aspect Aspect is not a significant factor Climatic features
The average annual precipitation is typically 14 to 20 inches, most of which occurs in the form of snow during the months of October through April. The soil temperature regime is frigid with the mean annual air temperature of about 45 degrees F. Temperature extremes range from 90 to -30 degrees F. The frost free period is 20 to 70 days. The optimum period for plant growth is from early May through mid-July.
Table 3 Representative climatic features
Frost-free period (average) 70 days Freeze-free period (average) 0 days Precipitation total (average) 20 in BarLineFigure 2. Monthly precipitation range
BarLineFigure 3. Monthly average minimum and maximum temperature
">Influencing water features
Soil features
The soils of this site are loamy, well drained and shallow to bedrock. The soils are typically associated with rock outcrops. Permeability is moderate. The available water holding capacity is about 1 to 3 inches. Runoff is medium to rapid. Erosion hazard by water is high.
Table 4. Representative soil features
Surface texture (1) Loam
Permeability class Moderate Available water capacity
(0-40in)1 – 3 in Ecological dynamics
Variablity in the plant composition and production results from variation in soil depth. Where soils are most shallow, plant production decreases and grasses tend to dominate in the understory. As soils deepen, big sagebrush and snowberry increase.
If the condition of the site deteriorates as a result of overgrazing, Idaho fescue decreases and big sagebrush increases. With prolonged abuse, lupine and other unpalatable forbs will increase. This site is likely to be invaded by lambsquarter and bull thistle. With heavy grazing pressure, seedling mortality of curlleaf mahogany is high and the stand will become even-aged and decadent.State and transition model
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Click on state and transition labels to scroll to the respective textEcosystem states
State 1 submodel, plant communities
State 1
HCPC, FEID/CELE3-ARTRVCommunity 1.1
HCPC, FEID/CELE3-ARTRVThe potential native plant community is dominated by curlleaf mountain mahogany with an understory of mountain big sagebrush, snowberry, and Idaho fescue. Vegetative composition is approximately 50% grasses, 5% forbs and 45% shrubs.
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 420 535 650 Shrub/Vine 230 405 580 Forb 50 80 110 Tree 40 70 100 Total 740 1090 1440 Figure 5. Plant community growth curve (percent production by month). OR5511 , D21 Low Elev., NA, Good Condition. RPC Growth Curve.
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 15 30 50 5 0 0 0 0 0 0 Additional community tables
Table 6. Community 1.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Grass/Grasslike1 Dominant deep rooted perennial grasses 400–600 Idaho fescue FEID Festuca idahoensis 400–600 – 5 Other perennial grasses 20–50 western needlegrass ACOC3 Achnatherum occidentale 0–5 – mountain brome BRMA4 Bromus marginatus 0–5 – Ross' sedge CARO5 Carex rossii 0–5 – squirreltail ELEL5 Elymus elymoides 0–5 – prairie Junegrass KOMA Koeleria macrantha 0–5 – basin wildrye LECI4 Leymus cinereus 0–5 – oniongrass MEBU Melica bulbosa 0–5 – Cusick's bluegrass POCU3 Poa cusickii 0–5 – Forb7 Dominant perennial forbs 40–80 agoseris AGOSE Agoseris 10–20 – arrowleaf balsamroot BASA3 Balsamorhiza sagittata 10–20 – tapertip hawksbeard CRAC2 Crepis acuminata 10–20 – lupine LUPIN Lupinus 10–20 – 9 Other perennial forbs 10–30 western hound's tongue CYOC Cynoglossum occidentale 0–5 – sulphur-flower buckwheat ERUM Eriogonum umbellatum 0–5 – phacelia PHACE Phacelia 0–5 – ragwort SENEC Senecio 0–5 – Shrub/Vine11 Dominant evergreen shrubs 20–100 mountain big sagebrush ARTRV Artemisia tridentata ssp. vaseyana 20–100 – 13 Dominant deciduous (or 1/2 shrubs) shrubs 170–380 curl-leaf mountain mahogany CELE3 Cercocarpus ledifolius 150–300 – common snowberry SYAL Symphoricarpos albus 20–80 – 14 Sub-dominant deciduous (or 1/2 shrubs) shrubs 20–50 green rabbitbrush ERTE18 Ericameria teretifolia 20–50 – 15 Other shrubs 20–50 chokecherry PRVI Prunus virginiana 0–5 – currant RIBES Ribes 0–5 – Tree16 Dominant evergreen trees 40–100 western juniper JUOC Juniperus occidentalis 20–50 – ponderosa pine PIPO Pinus ponderosa 20–50 – Interpretations
Animal community
This site offers food and cover to mule deer throughout the year. Sage grouse use this site extensively for food and cover.
Hydrological functions
The hydrologic soil group is D.
Wood products
A few scattered juniper and ponderosa pine provide a source of posts, poles, firewood, shade and diversity. Curlleaf mountain mahogany is a valuable novelty wood.
Other products
This site is suited to livestock grazing during summer and early fall under a planned grazing system.
Other information
Steep slopes and rock outcrops limit access by livestock and seedign equipment.
Supporting information
Type locality
Location 1: Klamath County, OR Township/Range/Section T39S R13E S20 General legal description Along Gerber road at edge of Langell Valley Rim T39S, R13E, Sec 20 Location 2: Klamath County, OR Township/Range/Section T38S R11E S24 General legal description Lower end of Rocky Canyon on Keno Springs road T38S, R11E, Sec 24 (E 1/2). Contributors
Barrett, Carlson
E Ersch
K.KennedyRangeland 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 Repp Contact for lead author Oregon NRCS State Rangeland Management Specialist Date 09/05/2012 Approved by Approval date Composition (Indicators 10 and 12) based on Annual Production Indicators
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Number and extent of rills:
Some, significant sheet & rill erosion hazard -
Presence of water flow patterns:
None to many on steeper slopes (up to 70%) -
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):
10-20% -
Number of gullies and erosion associated with gullies:
None -
Extent of wind scoured, blowouts and/or depositional areas:
None, slight wind erosion hazard -
Amount of litter movement (describe size and distance expected to travel):
Fine - slight wind erosion hazard -
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
Moderately to slightly resistant to erosion: aggregate stability = 3-5 -
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
Shallow, well drained loams, gravelly loams, and stony loams; associated with rock outcrops: Low OM (<1%) -
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
Moderate vegetative cover (45-55%) and gentle to very steep slopes (0-70%) effectively to moderately limit rainfall impact and overland flow; infiltration is moderate -
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:
Idaho fescue > Curlleaf maountain mahogany > Mountain big sagebrush > dominant shrubs > forbs > other grasses = other shrubs > Western JuniperSub-dominant:
Other:
Additional:
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Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
Normal decadence and mortality expected -
Average percent litter cover (%) and depth ( in):
-
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
Favorable: 1200, Normal: 1000, Unfavorable: 800 lbs/acre/year at high RSI (HCPC) -
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 brush species will increase with deterioration of plant community on the deeper soils. Western Juniper readily increases on the site. Cheatgrass and Medusahead invade sites that have lost deep rooted perennial grass functional groups. -
Perennial plant reproductive capability:
All species should be capable of reproducing annually
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