![SwLyc BRV](https://edit.jornada.nmsu.edu/uploads/large/pw/kz/1619541992_318160.jpg)
Shallow Loamy Calcareous Bear River Valley 10-14" P.Z.
Scenario model
Current ecosystem state
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Management practices/drivers
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Transition T1-2
Herbivory (continuous or season-long, low to moderate stocking)
More details -
No transition or restoration pathway between the selected states has been described
Target ecosystem state
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Description
The Reference State consists of two plant communities: the Black Sagebrush/Bunchgrass Plant Community (1.1.1) and the Bunchgrass/Black Sagebrush Plant Community (1.1.2). Each plant community differs in percent composition and foliar cover of bunchgrasses and black sagebrush (Artemisia nova) as the dominant shrub. Forbs are a minor component.
Two important processes occur in the reference state and result in plant community changes: 1) sagebrush-killing disturbances such as fire, herbivory, drought, and flood; and 2) time without those disturbances, generally referred to as "natural succession."
Characteristics and indicators
The shift between plant community phases is dependent upon sagebrush-killing disturbances, and without them sagebrush will increase even with proper grazing management. Improper grazing management may accelerate the rate of increase for the shrub component.
Management actions or treatments are not prescribed or used to mimic the natural disturbance regime due to fragile nature of the soils and lower productivity potential on this site. Prescribed fire is not used due to land use and ownership patterns and lack of fine fuels (Clause and Randall, 2014).
Resilience management
This site has moderate resilience due to its xeric soil moisture regime and frigid temperature regime (Chambers et.al. 2014). Precipitation is typically adequate and more effective with cooler temperatures, but timing of precipitation lowers resilience. Moisture is often not present when needed to support recovery efforts. The site can usually recovery after disturbance but is susceptible to delays in recovery during extreme climatic events such as drought.
The site has moderately low resistance to invasion by annual grasses because of climate suitability. Winter precipitation patterns favor annual invasion while cooler temperatures provide some resistance. The site is susceptible to invasion during hotter climatic periods.
On the LRU scale, this site is more resistant to invasion by annual grasses due soil chemistry, mainly its calcium carbonate (CaCO3) equivalent greater than 15 percent.
Submodel
Description
The Grazing Resistant State has seen a shift in under-story functional/structural group dominance. Due to herbivory pressure, there is a shift from mid-stature cool-season bunchgrasses to short-stature cool-season bunchgrasses such as Sandberg bluegrass and rhizomatous wheatgrasses like thickspike wheatgrass and western wheatgrass. Mat-forming forbs such as pussytoes (Antennaria spp.), Hood's phlox (Phlox hoodii), and buckwheat (Eriogonum spp.) increase and can become dominant on the sites.
Characteristics and indicators
There are fewer mid-size bunchgrasses and they are typically found under the shrub canopy where they are protected from herbivory. The shrub canopy inter-spaces are occupied by grazing tolerant grasses as well as mat-forming forbs. Drier site conditions result in lower productivity and less herbaceous production potential. Surface rock fragments and mat-forming species typically armor the site and protect it from soil erosion.
In many cases, the transition to the Grazing Resistant State may have occurred many decades ago during an era of higher stocking rates and continuous grazing during the growing season. However, continual grazing during the critical growth period (roughly May-June) at proper stocking rates will facilitate the transition to this state and maintain it as a stable state.
Resilience management
Site resilience is lower than the Reference State. Site hydrology has been modified due to moisture being utilized by shallower rooting species. Therefore, the site is drier earlier in the season and unable to recover as quickly after a disturbance. This state is more drought-prone, and therefore more vulnerable to invasion by annual invasive species. However, existing sagebrush canopy and remnant perennial vegetation provide some amount of resiliency.
Rhizomatous grasses form mats that provide soil protection by protecting the soil from raindrop impact, decreasing the risk of soil erosion. However, overall soil stability is lower than the reference state, primarily due to a reduction in soil organic matter due to a reduction in litter.
Site resistance to invasion by annual grasses is lower due to niches in the under-story for establishment as well as site water availability during the time suited for winter annuals such as cheatgrass (Bromus tectorum). Episodic and limited moisture is more suited to annual life forms. However, high calcium carbonate equivalent (CCE) soil chemistry adds additional resistance to invasion.
Submodel
Mechanism
Herbivory pressure in excess of normal Reference State conditions. A typical scenario is continuous spring or season-long grazing with low stocking intensity.
Constraints to recovery
Recovery is inhibited by continued herbivory pressure, reduced seedbank, and drought conditions. Annual grasses are likely in small amounts.
Context dependence
Drought and annual invasion are most likely variables to prevent restoration.
Model keys
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The 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.