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Draft. A draft ecological site description is either incomplete or has not undergone quality control and quality assurance review.
Table 1. Dominant plant species
Tree Not specified
Shrub Not specified
Herbaceous Not specified
Physiographic features
Table 2. Representative physiographic features
Climatic features
">Influencing water features
Soil features
Ecological dynamics
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, LETR5/SAVE4Community 1.1
HCPC, LETR5/SAVE4!
Figure 1. Annual production by plant type (representative values) or group (midpoint values)
Table 3. Annual production by plant type
Plant type Low
(lb/acre)Representative value
(lb/acre)High
(lb/acre)Grass/Grasslike 378 431 483 Shrub/Vine 231 259 287 Forb 28 35 42 Total 637 725 812 Additional community tables
Table 4. Community 1.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Grass/Grasslike1 Dominant deep rooted perennial grasses 350–420 beardless wildrye LETR5 Leymus triticoides 350–420 – 2 Sub-dominant deep rooted perennial grasses 21–49 basin wildrye LECI4 Leymus cinereus 14–35 – Indian ricegrass ACHY Achnatherum hymenoides 7–14 – 4 Sub-dominant shallow rooted perennial grasses 7–14 saltgrass DISP Distichlis spicata 7–14 – Forb7 Dominant perennial forbs 14–21 milkvetch ASTRA Astragalus 14–21 – 9 Other perennial forbs 14–21 Shrub/Vine13 Dominant deciduous (or 1/2 shrubs) shrubs 210–245 greasewood SAVE4 Sarcobatus vermiculatus 210–245 – 14 Sub-dominant deciduous (or 1/2 shrubs) shrubs 21–42 rubber rabbitbrush ERNA10 Ericameria nauseosa 7–14 – spiny hopsage GRSP Grayia spinosa 7–14 – shortspine horsebrush TESP2 Tetradymia spinosa 7–14 – Interpretations
Supporting information
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 08/21/2012 Approved by Approval date Composition (Indicators 10 and 12) based on Annual Production Indicators
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Number and extent of rills:
None, slight sheet & rill erosion hazard -
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):
15-30% -
Number of gullies and erosion associated with gullies:
None -
Extent of wind scoured, blowouts and/or depositional areas:
Few to many, significant wind erosion hazard -
Amount of litter movement (describe size and distance expected to travel):
Fine - limited movement -
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
Slightly resistant to erosion: aggregate stability = 1-3 -
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
Very deep, well drained beach ridges and dunes of ashy loam or sandy loam: Low OM (<1.0%) -
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
Limited ground cover (10-25%), large areas of bare soil, and gentle slopes (0-10%) provide minimal protection from rainfall impact and overland flow; infiltration rates are high -
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:
Creeping wildrye > Black greasewood > Basin wildrye > other grasses = forbs > other shrubsSub-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: 900, Normal: 700, Unfavorable: 500 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. 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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