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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
R023XY116OR SEMI-WET MARSH
Semi-Wet Marsh
R023XY117OR BASIN WET MEADOW
Basin Wet Meadow
R023XY118OR BASIN DRY MEADOW
Basin Dry Meadow
Similar sites
R023XY116OR SEMI-WET MARSH
Semi-Wet Marsh (ponding depth and duration less)
Table 1. Dominant plant species
Tree Not specified
Shrub Not specified
Herbaceous (1) Schoenoplectus acutus
(2) Sparganium eurycarpumPhysiographic features
This site occurs in basins and valleys on the floodplains of perennial drainage systems. Slopes range from 0 to 1 percent. Elevation ranges from 4000 to 4500 feet.
Table 2. Representative physiographic features
Landforms (1) Flood plain
(2) Basin floor
(3) Valley floor
Ponding duration Long (7 to 30 days) Ponding frequency Frequent Elevation 4000 – 4500 ft Slope 0 – 1 % Ponding depth 24 – 36 in Water table depth 30 in Aspect Aspect is not a significant factor Climatic features
The annual precipitation ranges from 8 to 12 inches, most of which occurs between the months of December through March. The mean annual air temperature is 48 degrees F. Temperature extremes range from 110 to -30 degrees F. The period of optimum plant growth is from the first of April through June.
Table 3 Representative climatic features
Frost-free period (average) 0 days Freeze-free period (average) 0 days Precipitation total (average) 10 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 very deep and very poorly drained. Ponding to depths of 2 to 3 feet above the soil surface is frequent from March to July. A permanent water table occurs at a depth of 30 inches below the soil surface. Surface and subsurface textures vary from muck to mucky silt loams. Often there is a sand layer at approximately 5 feet.
Table 4. Representative soil features
Surface texture (1) Silt loam
Family particle size (1) Sandy
Drainage class Poorly drained Permeability class Moderate Ecological dynamics
Range in Characteristics:
Variation in plant composition and production results from depth and duration of surface ponding. Hardstem bulrush has a broad range, occupying the deepest ponded areas as well as shallow areas while broadfruit burreed can withstand prolonged submergence to depths of 2.5 to 3 feet, conditions that eliminates cattails. Cattails on the otherhand, germinate earlier and can withstand longer dry periods. As a result, hardstem bulrush and broadfruit burreed occur as pure stands in deeper ponded areas while cattails increase in shallower ponded areas.
Response to Disturbance:
If the extent and duration of ponding is reduced to critical levels through water regulation or drainage, extensive changes to dry site conditions will result. Under initial drying conditions, broadfruit burreed, a very sensitive species, will disappear and hardstem bulrush will decrease. Reed canarygrass will strongly invade and cattails will increase. With continued drying and/or disturbance reed canarygrass will dominate the site. Perennial pepperweed and Canadian thistle will also invade.
With ponding to depths greater than 3 feet or burning plus extended ponding, the amount of bulrush, burreed, and other species will be reduced. This occurs because emerged stems are necessary for air transport to submerged stems, crowns, and roots. If water drawdown occurs after deep ponding and mudflats develop, smartweeds, lamb's quarter, goosefoot, and pigweed often invade.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
Reference StateCommunity 1.1
Reference Plant CommunityThe potential native plant community is strongly dominated by hardstem bulrush and broadfruit burreed in a pattern arrangement. Other vegetation is minor. The potential vegetative composition is approximately 50 percent bulrush and 40 percent burreed. Approximate ground cover is 90-120 percent (basal and crown).
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)Forb 1500 2000 3000 Grass/Grasslike 1500 2000 3000 Total 3000 4000 6000 Additional community tables
Table 6. Community 1.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Grass/Grasslike1 Perennial, deep-rooted, rhizomatous, bulrush 1600–2400 hardstem bulrush SCAC3 Schoenoplectus acutus 1600–2400 – 2 Perennial, deep-rooted, rhizomatous grass-like 0–1000 softstem bulrush SCTA2 Schoenoplectus tabernaemontani 0–400 – common reed PHAU7 Phragmites australis 0–200 – sedge CAREX Carex 0–200 – spikerush ELEOC Eleocharis 0–200 – Forb7 Perennial, erect, rhizomatous, monocot 1600–2400 broadfruit bur-reed SPEU Sparganium eurycarpum 1600–2400 – 8 Perennial, erect, rhizomatous, monocot 120–400 broadleaf cattail TYLA Typha latifolia 120–400 – 9 Other perennial forbs 120–240 water plantain ALISM Alisma 0–120 – arrowhead SAGIT Sagittaria 0–120 – Interpretations
Animal community
Livestock Grazing:
Portions of this site that dry in the fall have limited suitability for cattle use. Ponding precludes use for the remainder of the year.
Native Wildlife Associated with the Climax Community:
Numerous waterfowl including sandhill cranes, diving ducks (redhead and canvas backs), black terns, and mallards use this site for nesting, brooding, food and/or cover. Burreed, the key species, provides the preferred nesting areas and brood cover. Burreed and bulrush are both preferred over cattails for nesting cover. When dry or frozen, deer utilize this site for winter cover and food.Hydrological functions
The hydrologic cover condition is good when the ecological condition is high.
Other information
If there is adequate organic matter depth in the surface (approximately 2 feet), this site may be dried, burned, and reflooded to create more open water. This site is a Type 4 wetland (Inland Deep Fresh Marsh).
Supporting information
Contributors
A V Bahn
Bob Gillaspy
M. ParksRangeland 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 08/09/2012 Approved by Approval date Composition (Indicators 10 and 12) based on Annual Production Indicators
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Number and extent of rills:
None -
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):
0-5% -
Number of gullies and erosion associated with gullies:
None -
Extent of wind scoured, blowouts and/or depositional areas:
None, moderate wind erosion hazard -
Amount of litter movement (describe size and distance expected to travel):
Fine to moderately coarse - limited movement -
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
Moderately to significantly resistant to erosion: aggregate stability = 4-6 -
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
Very deep poorly drained silt loam to muck: Moderate to high OM (3-6%) -
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
Significant ground cover (90-120%) and gentle slopes (0-1%) effectively limit rainfall impact and overland flow -
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:
Hardstem Bulrush > Broadfruit Burrees > other emergent grass-likes > other emergent forbsSub-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: 6000, Normal: 4000, Unfavorable: 3000 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:
Cattail species will increase with deterioration of plant community. Reed canarygrass, Meadow foxtail, Kentucky bluegrass, thistles, perennial pepperweed, and foxtail barley 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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PrintThe Ecosystem Dynamics Interpretive Tool is an information system framework developed by the USDA-ARS Jornada Experimental Range, USDA Natural Resources Conservation Service, and New Mexico State University.
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