Coarse Upland 20-24 Inch Precipitation Zone Lost River Mountains
Scenario model
Current ecosystem state
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Management practices/drivers
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- Transition T1A More details
- Transition T1B More details
- Restoration pathway R2A More details
- Restoration pathway R3A More details
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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 of the Coarse Upland 20-24 Inch Precipitation Zone ecological site consists of three major plant communities. All three of these communities have a shrub overstory that is dominated by mountain big sagebrush (Artemisia tridentata ssp. vaseyana). The difference between the communities is expressed through the composition and foliar cover of understory species. The primary community of the Reference state has an understory dominated by Idaho fescue (Festuca idahoensis). The other two communities have understories dominated by either bluebunch wheatgrass (Pseudoroegneria spicata) or a combination of Idaho fescue and Geyer's sedge (Carex geyeri).
Processes (both natural and anthropogenic) that result in state and community changes include fire, grazing, land use change, and occurrence of invasive species.
Characteristics and indicators
The indicators showing a shift between communities in the Reference state are driven by composition and foliar cover of grass species. In the primary community, Idaho fescue is the most prominent understory grass species, both in foliar cover and contribution to annual production. Community 1.2 has a higher canopy cover of bluebunch wheatgrass, however Idaho fescue may still be present at varying extents. The understory of Community 1.3 will have Geyer's sedge present, usually co-dominating the understory with Idaho fescue.
Low-severity disturbances and slight differences in localized conditions are the primary drivers influencing the understory canopy cover of grass species. Severe or frequent fire disturbances at sites tend to shift towards more fire-resilient and resistant species such as Geyer's sedge and bluebunch wheatgrass. Sites found at the higher end of the effective precipitation range tend to favor Communities 1.1 and 1.3.
Resilience management
The Reference state is overall moderately resilient. In well-established communities, resilience towards climatic disturbances such as drought is high. Existing in the 20 to 24-inch effective precipitation range aids in resistance to drought conditions and communities 1.1 and 1.2 are comprised of many drought-resistance species.
Resilience to moderate or high-severity fire is low. Mountain big sagebrush produces large quantities of fine fuel and is susceptible to stand-destroying fires. If the disturbance is severe enough, this can initiate the transition from the Reference state to the Disturbed state.
Submodel
Description
The Grazed state of this ecological site has one major community. The Grazed state is a mechanism of chronic defoliation from grazing pressure by agricultural grazing, natural grazing, or a combination of the two. The transition from the Reference state to the Grazed state occurs when understory grasses of the Reference state, such as Idaho fescue and bluebunch wheatgrass experience chronic defoliation to the point that they are replaced by more grazing-tolerant species such as Sandberg bluegrass (Poa secunda) and rhizomatous wheatgrasses. Without managed grazing and rest, it is difficult to restore this state to the reference.
Production in this state is lower and shifts more towards the shrub functional group. This state is also more susceptible to invasive species establishment resulting from the removal of Reference state species competition and hoof disturbance to the soil.
Characteristics and indicators
The primary indicator of the Grazed state is a shift in the compositional structure of the understory grass species. The bunchgrasses found in the Reference state (bluebunch wheatgrass and Idaho fescue) are removed through chronic defoliation and replaced with more grazing-tolerant species such as Sandberg bluegrass and rhizomatous wheatgrasses. There is often also an increase in invasive species in this state as opportunities for establishment are created as the native species decrease. Soil disturbance from hoof traffic can also increase invasive species recruitment.
Resilience management
The Grazed state is moderately resilient. Most species present in this state are drought tolerant and response to frequent or severe fire varies by plant. Replacement of native vegetation through chronic defoliation from grazing increases opportunities for invasive species to establish. The greater the canopy cover of invasive species, the lower the resilience of the site.
Submodel
Description
The Disturbance state occurs when a natural or anthropogenic disturbance removes the overstory vegetation of the ecological site. These disturbances can include severe or frequent fire, flooding, prolonged periods of drought, intense grazing with hoof-related disturbance, insect and disease, and mechanical removal. The most common disturbance to impact this ecological site is severe or frequent fire. Fire removes the shrub overstory and the grass and forb functional groups become solely dominant. This can occur in small patches of a mosaic burn pattern, or in large spatial areas from severe fire events.
Characteristics and indicators
The Disturbance state is indicated by a lack of shrub overstory or a shrub overstory that consists of disturbance-tolerant species such as yellow rabbitbrush (Chrysothamnus viscidiflorus). The understory can maintain many of the bunchgrasses and forbs found in the Reference state such as Idaho fescue, bluebunch wheatgrass, and prairie Junegrass which recover much more quickly following disturbance events. The composition of this state may also include invasive species as the disturbance opens opportunities for establishment.
Resilience management
This state is moderately resilient. Many species found in this state are drought tolerant. Continued disturbance can perpetuate this state, increasing time before the overstory is able to recover to pre-disturbance canopy structure and composition. This state loses resilience as a result of increased invasive species establishment following a disturbance.
Submodel
Mechanism
Transition from the Reference state to the Grazed state is a mechanism of intensive grazing practices that result in chronic defoliation of the understory vegetation. Over time, species like bluebunch wheatgrass and Idaho fescue are not able to recover from defoliation and the total canopy cover of that species will decrease on a site. In the absence of these species, grazing-tolerant plants such as Sandberg bluegrass will increase in canopy cover and production. The remaining bluebunch wheatgrass and Idaho fescue will be concentrated under the overstory shrub cover.
Constraints to recovery
Constraints to recovery include:
o Continued improper grazing techniques that result in chronic defoliation of vegetation
o Prolonged periods of drought that diminish regeneration of desired species
o Loss of nutrient-rich topsoil due to increased erosion
o Establishment of invasive species
Context dependence
Restoration efforts can be greatly influenced by precipitation patterns. Successful regeneration of Reference state understory species is highly dependent on moisture received post-restoration efforts. Rates of successful establishment of Idaho fescue and bluebunch wheatgrass increase when available moisture is high during critical regeneration periods (Zlatnik, 1999; Howard, 1997).
Mechanism
The transition from the Reference state to the Disturbed state is a mechanism of frequent or severe disturbances that remove the overstory shrubs on a given site. The most common disturbance that results in the loss of the shrub overstory is high-intensity fire. Mountain big sagebrush is sensitive to all but the lowest severity fire, generally resulting in stand replacement. Since 1900, fire exclusion and removal of fine fuels through grazing have increased fire return intervals and increased the likelihood of more severe fire events that are often stand-destroying (Innes, 2017).
Constraints to recovery
Constraints to recovery include:
o Frequent disturbances before recovery have completed
o Prolonged periods of drought that diminish regeneration of desired species
o Loss of nutrient-rich topsoil due to increased erosion
o Establishment of invasive species
o Distance from seed source
Context dependence
The primary factor driving the likelihood of restoration success is post disturbance weather patterns. Prolonged periods of drought can slow restoration processes, whereas average to above-average precipitation post-disturbance can greatly increase speed and success in the re-establishment of Reference state species (Steinberg, 2002; Fryer, 2009).
Mountain big sagebrush recovery time can also be dependent on the extent of disturbance and accordingly, distance from seed source (Innes, 2017).
Mechanism
The primary mechanism for restoration from the Grazed state to the Reference state is rest from grazing. Reference state grasses such as bluebunch wheatgrass and Idaho fescue will not be able to re-establish while grazing pressure continues. Seeding of desired species may speed up the restoration process.
Context dependence
The time frame for restoration is highly dependent on variations in localized weather patterns. Prolonged periods of drought can dramatically increase the time required to return to the Reference state, whereas periods of above-normal precipitation can decrease that time frame.
Light-intensity and infrequent grazing events that mimic natural historic grazing patterns will not impact the restoration pathway. However, continuous early-season grazing at moderate to high intensity resulting in significant defoliation will perpetuate the Grazed state.
Mechanism
Restoration from the Disturbed state to the Reference state is a mechanism of time without stand-destroying disturbance. If the shrub overstory is removed, replacement seedlings will need to reach maturity without any further disturbances.
Context dependence
The speed of restoration to the Reference state is dependent on the distance form the seed source and conditions following the disturbance. Seasons of higher than average annual precipitation following the disturbance can create conditions favorable to recovery. Planting or seeding of Reference state species can speed recovery and help prevent the establishment of invasive species.
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