Semi-desert Loamy Run-on (Basin big sagebrush/ Mixed bunchgrass)
Scenario model
Current ecosystem state
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Management practices/drivers
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Transition T1A
The simultaneous introduction of exotic species, both plants and animals, and possible extinctions of native flora and fauna, along with climate change
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Transition T2A
Long periods (several decades) without fire and/or heavy grazing, especially during the growing season of grasses
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Transition T2B
Relatively hot (stand-replacing) wildfire followed by heavy growing season grazing disturbances
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Restoration pathway R3A
Brush management, seeding, prescribed grazing
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Transition T3A
Wildfire or brush management followed by heavy grazing
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Restoration pathway R4A
Brush management, seeding, prescribed grazing
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No transition or restoration pathway between the selected states has been described
Target ecosystem state
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Description
The Reference State is a description of this ecological site just prior to Euro-American settlement but long after the arrival of Native Americans. The description of the Reference State was determined by NRCS Soil Survey Type Site Location information and familiarity with rangeland relict areas where they exist. Pre-settlement fire return intervals of 20 to 30 years tended to favor the native bunchgrasses. Under such conditions, the native plant community would have been characterized by mixed bunchgrasses and basin big sagebrush (Artemisia tridentata ssp. tridentata) (2.1). The major grasses would have included basin wildrye (Leymus cinereus), rhizomatous bluebunch wheatgrass (Pseudoroegneria spicata), bottlebrush squirreltail (Elymus elymoides), native bluegrasses (Poa secunda, Poa fendleriana), and thickspike wheatgrass (Elymus lanceolatus). Other associated woody species may have included yellow rabbitbrush (Chrysothamnus viscidiflorus) and winterfat (Krascheninnikovia lanata). A more complete list of species by lifeform for the Reference State is available in the accompanying tables in the “Plant Community Composition by Weight and Percentage” section of this document.
Submodel
Description
State 2 is very similar to State 1 in form and function, with the exception of the presence of non-native plants and animals, possible extinctions of native species, and a different climate. State 2 is a description of the ecological site shortly following Euro-American settlement. This State can be regarded as the current potential. The range in plant communities within this State is characterized by the relative amount of bunchgrass present, which is primarily associated with the time since last fire. With more recent fires and prescribed grazing (2.2a) the plant community would be dominated by mixed bunchgrasses and basin big sagebrush (2.1). In the absence of fire and with protection from livestock grazing (2.1a), the plant community would shift to a more basin big sagebrush dominated site, but would still have remnants of the native bunchgrass understory (2.2).
Resiliency of this State is maintained by the availability of native seed sources for both the mixed bunchgrasses and basin big sagebrush, and by wildfire. This site responds well to cool season fire and more moderate non-growing season grazing regimes provided that the seed sources for the mixed bunchgrasses are present. A pre-settlement fire return interval of 20-30 years favored the grasses. Without fire, bunchgrass diversity and production may diminish, while sagebrush may increase and ultimately outcompete the native bunchgrasses. This shift in plant community composition puts this State at greater risk in the event of a hot summer or fall fire; further degradation could occur if grazing were to be initiated immediately following such a fire. Hotter fires followed by heavy grazing could cause the replacement of the basin big sagebrush component with fire-tolerant species such as yellow rabbitbrush and rhizomatous wheatgrasses.
Submodel
Description
State 3: Basin Big Sagebrush/ Rhizomatous Wheatgrass State
Sites where heavy continuous season-long grazing has taken place in the absence of fire will develop into a basin big sagebrush-dominated plant community accompanied by rhizomatous bluebunch and western wheatgrasses. Resiliency of this State is maintained by the absence of fire and heavy grazing during the growing season for grasses, which removes grazing-intolerant grass species (bunchgrasses) and leaves only grazing-tolerant grasses and sagebrush. The dominance of basin big sagebrush and lack of native bunchgrasses places this State at risk in the event of a hot summer or fall fire.
Submodel
Description
Yellow rabbitbrush and rhizomatous wheatgrass will be found on sites that have experienced both heavy continuous season-long grazing and frequent wildfire disturbances. This is the most commonly found current State. The resiliency of this State is maintained by the ability of root-sprouting species (yellow rabbitbrush and rhizomatous wheatgrasses) to successfully establish after fire and out-compete other fire and grazing-intolerant species.
Submodel
Mechanism
Transition T1a: from State 1 to State 2 (Reference State to Basin Big Sagebrush/ Mixed Bunchgrass/ Introduced Non-natives State)
The simultaneous introduction of exotic species, both plants and animals, and possible extinctions of native flora and fauna, along with climate change, caused State 1 to transition to State 2. Reversal of such historic changes (i.e. a return pathway) back to State 1 is not practical.
Mechanism
Transition T2a: from State 2 to State 3 (Basin Big Sagebrush/ Mixed Bunchgrass/ Introduced Non-natives State to Basin Big Sagebrush/ Rhizomatous Wheatgrass State)
The Mixed Bunchgrass/ Basin Big Sagebrush/ Introduced Non-natives State will transition to the Basin Big Sagebrush/ Rhizomatous Wheatgrass State in the absence of fire or with heavy grazing during the growing season of grasses, removing grazing intolerant species. The approach to this transition is indicated by an increase in basin big sagebrush cover, height, and age relative to grasses. Long periods (several decades) without fire and/or heavy grazing, especially during the growing season of grasses, will trigger the transition.
Mechanism
Transition T2b: from State 2 to State 4 (Basin Big Sagebrush/ Mixed Bunchgrass/ Introduced Non-natives State to Yellow Rabbitbrush/ Rhizomatous Wheatgrass State)
The Mixed Bunchgrass/ Basin Big Sagebrush/ Introduced Herb State transition to the Yellow Rabbitbrush/ Rhizomatous Wheatgrass State is triggered by a relatively hot (stand-replacing) wildfire followed by heavy growing season grazing disturbances which remove remaining (post-fire) grazing intolerant grass species. The approach to this transition is indicated by an increase in basin big sagebrush cover, height, and age relative to grasses.
Mechanism
Restoration Pathway R3a: from State 3 to State 2 (Basin Big Sagebrush/ Rhizomatous Wheatgrass State to Mixed Bunchgrass/ Basin Big Sagebrush/ Introduced Non-natives State)
It may be possible using a combination of brush management (e.g. chemicals, low tillage, mechanical methods via Lawson soil aerator, or prescribed fire), prescribed grazing, and reseeding with native bunchgrasses to restore this plant community to conditions associated with the Basin Big Sagebrush/ Mixed Bunchgrass/ Introduced Herb State (State 2).
Mechanism
Transition 3a: from State 3 to State 4 (Basin Big Sagebrush/Rhizomatous Wheatgrass State to Yellow Rabbitbrush/ Rhizomatous Wheatgrass State)
The Basin Big Sagebrush/Rhizomatous Wheatgrass State transition to the Yellow Rabbitbrush/Rhizomatous Wheatgrass State is triggered by a hot (stand-replacing) wildfire or brush management techniques (e.g. chemical, mechanical, fire), followed by heavy grazing during growing season of the grasses in close temporal proximity. The approach to this transition is indicated by an increase in basin big sagebrush cover, height, and age, and by an increase in the continuity of understory fuels.
Mechanism
Restoration Pathway R4a: from State 4 to State 2 (Yellow Rabbitbrush/ Rhizomatous Wheatgrass State to Basin Big Sagebrush/ Mixed Bunchgrass/ Introduced Herb State)
It may be possible using a combination of brush management (e.g. using chemicals), inter-seeding with native bunchgrasses, and prescribed grazing to restore this plant community to conditions associated with the Basin Big Sagebrush/ Mixed Bunchgrass/ Introduced Non-natives State if accelerated soil erosion or soil tillage has not taken place. Tillage eliminates the native perennial forbs, some of which are very difficult to replace because their seed is either very expensive or unavailable.
Model keys
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