Sandy Claypan
Scenario model
Current ecosystem state
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Management practices/drivers
Select a transition or restoration pathway
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Transition T1A
Introduction of exotic cool-season grasses
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Transition T2A
Heavy grazing with multiyear drought
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Transition T2B
Long-term non-use or light utilization, and no fire
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Restoration pathway R3A
Successful grazing land mechanical treatment
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Transition T3A
Late season grazing, long-term non-use, or light utilization, and no fire
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Restoration pathway R4A
Long-term prescribed grazing and prescribed burning
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Restoration pathway R5A
Successful range planting
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Restoration pathway R5B
Failed range planting and/or secondary succession
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Restoration pathway T6A
Cessation of annual cropping
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No transition or restoration pathway between the selected states has been described
Target ecosystem state
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Description
This state represents the natural range of variability that dominated the dynamics of this ecological site prior to European influence. The primary disturbance mechanisms for this site in the reference condition included frequent fire and grazing by large herding ungulates. Timing of fires and grazing, coupled with weather events, dictated the dynamics that occurred within the natural range of variability. These factors likely caused the community to shift both spatially and temporally between two community phases.
Characteristics and indicators
Because of changes in disturbances and other environmental factors (particularly the widespread occurrence of exotic species), the Reference State is considered to no longer exist.
Resilience management
If intact, the reference state should probably be managed with current disturbance regimes which has permitted the site to remain in reference condition as well as maintaining the quality and integrity of associated ecological sites. Maintenance of the reference condition is contingent upon a monitoring protocol to guide management.
Submodel
Description
This state is similar to State 1: Reference State but has now been colonized by the exotic cool-season grasses (e.g., Kentucky bluegrass, smooth brome, crested wheatgrass, annual bromes) which are now present in small amounts. Although the state is still dominated by native grasses, an increase in these exotic cool-season grasses can be expected.
These exotic cool-season grasses can be quite invasive on the site and are particularly well adapted to heavy grazing. They also often form monotypic stands. As these exotic cool-season grasses increase, both forage quantity and quality become increasingly restricted to late spring and early summer due to the monotypic nature of the stand, even though annual production may increase. Native forbs generally decrease in production, abundance, diversity, and richness compared to that of State 1: Reference State.
These exotic cool-season grasses have been particularly and consistently invasive under extended periods of no use and no fire. To slow or limit the invasion of these exotic grasses, it is imperative that managerial techniques (e.g., prescribed grazing, prescribed burning) be carefully constructed, monitored, and evaluated with respect to that objective. If management does not include measures to control or reduce these exotic cool-season grasses, the transition to State 4: Invaded State should be expected (T2B).
Annual production of this state can be quite variable, in large part due to the amount of exotic cool-season grasses. However, as the exotic cool-season grasses increase peak production will shift to earlier in the growing season.
Characteristics and indicators
The presence of trace amounts of exotic cool-season grasses indicates a transition from State 1 to State 2. The presence of exotic biennial or perennial leguminous forbs (i.e., sweet clover, black medic) may not, on their own, indicate a transition from State 1 to State 2 but may facilitate that transition.
Resilience management
To slow or limit the invasion of these exotic grasses, it is imperative that managerial techniques (e.g., prescribed grazing, prescribed burning) be carefully constructed, monitored, and evaluated with respect to that objective.
Grazing management should be applied that enhances the competitive advantage of native grass and forb species. This may include: (1) early spring grazing when exotic cool-season grasses are actively growing and native cool-season grasses are dormant; (2) applying proper deferment periods allowing native grasses to recover and maintain or improve vigor; (3) adjusting overall grazing intensity to reduce excessive plant litter (above that needed for rangeland health indicator #14 – see Rangeland Health Reference Worksheet); (4) incorporating early heavy spring utilization which focuses grazing pressure on exotic cool-season grasses and reduces plant litter, provided that livestock are moved when grazing selection shifts from exotic cool-season grasses to native grasses.
Prescribed burning should be applied in a manner that maintains or enhances the competitive advantage of native grass and forb species. Prescribed burns should be applied as needed to adequately reduce/remove excessive plant litter and maintain the competitive advantage for native species. Timing of prescribed burns (spring vs. summer vs. fall) should be adjusted to account for differences in annual growing conditions and applied during windows of opportunity to best shift the competitive advantage to the native species.
Submodel
Description
This state often results from multiyear drought coupled with long-term heavy grazing. As a result, shortgrasses (e.g., blue grama), upland sedges, and lesser spikemoss become dominant. Lesser spikemoss soil surface cover is often 25% or greater. Once the state is well established, mechanical as well as other treatments have been largely ineffective in suppressing or eliminating it, even though some short-term reductions may appear successful. As a result, the restoration pathway to State 2: Native/Invaded State (R3A) will likely be temporary.
Characteristics and indicators
This site is characterized by lesser spikemoss occupying plant interspaces and prevalence of shortgrasses (i.e., blue grama) and sedges.
Resilience management
This plant community is resilient and resistant to most management techniques. Overgrazing with/without drought will maintain this state.
Submodel
Description
This state is the result of invasion and dominance by the exotic cool-season grasses (commonly Kentucky bluegrass, smooth brome, crested wheatgrass, and/or annual bromes). Exotic forbs (e.g., Canada thistle, leafy spurge) may also invade the site. The exotic cool-season grasses can be quite invasive on the site and are particularly well adapted to heavy grazing. They also often form monotypic stands. As these exotic cool- season grasses increase, both forage quantity and quality become increasingly restricted to late spring and early summer due to the monotypic nature of the stand, even though annual production may increase. Native forbs generally decrease in production, abundance, diversity, and richness compared to that of State 1: Reference State. Common forbs often include hairy false goldenaster, goldenrod, common yarrow, and white sagebrush. Shrubs, such as western snowberry and rose, may show marked increases. Once the state is well established, prescribed burning and grazing techniques have been largely ineffective in suppressing or eliminating the exotic species, even though some short-term reductions may appear successful.
Annual production of this state may vary widely, in part due to variations in the extent of invasion by exotic cool-season grasses. However, as the exotic cool-season grasses increase, peak production will shift to earlier in the growing season.
Characteristics and indicators
This site is characterized by exotic cool-season grasses constituting greater than 30 percent of the annual production and native grasses constituting less than 40 percent of the annual production.
Resilience management
Light or moderately stocked continuous, season-long grazing or a prescribed grazing system which incorporates adequate deferment periods between grazing events and proper stocking rate levels will maintain this State. Application of herbaceous weed treatment, occasional prescribed burning and/or brush management may be needed to manage noxious weeds and increasing shrub (e.g., western snowberry) populations.
Submodel
Description
This state is highly variable depending on the level and duration of disturbance related to the T6A transitional pathway (e.g., cropping, recreational activity, or concentrated livestock activity for a prolonged period). Following cessation of disturbances, the plant community will initially include a variety of annual forbs and grasses (some of which may be noxious weeds and need control). Over time, the exotic cool-season grasses (e.g., Kentucky bluegrass, smooth brome, crested wheatgrass, smooth brome, annual bromes) will likely predominate.
Characteristics and indicators
Tillage has destroyed the native plant community, altered soil structure and biology, reduced soil organic matter, and resulted in the formation of a tillage induced compacted layer which is restrictive to root growth. Removal of perennial grasses and forbs results in decreased infiltration and increased runoff.
Resilience management
Continued tillage will maintain the state. Control of noxious weeds will be required.
Submodel
Mechanism
This is the transition from the State 1: Reference State to the State 2: Native/Invaded State due to the introduction and establishment of exotic cool-season grasses (e.g., Kentucky bluegrass, smooth brome, crested wheatgrass, annual bromes). This transition was probably inevitable and corresponded to a decline in native warm-season and cool-season grasses; it may have been exacerbated by chronic season-long or heavy late season grazing. Complete rest from grazing and suppression of fire could also have hastened the transition. The threshold between states was crossed when Kentucky bluegrass, smooth brome, crested wheatgrass, annual bromes, or other exotic species became established on the site.
Constraints to recovery
Current knowledge and technology will not facilitate a successful restoration to Reference State.
Mechanism
The transition from State 2: Native/Invaded State to State 3: Shortgrass State occurs with heavy grazing with multiyear drought leading to the site becoming dominated by short-statured warm-season grasses (e.g., blue grama), along with sedges, forbs, and lesser spikemoss. Lesser spikemoss is prevalent in the western portion of the MLRA, while the eastern portion is characterized by dense blue grama sod.
Constraints to recovery
Variations in growing conditions (e.g., cool, wet spring) will influence effects of various management activities on exotic cool-season grass populations.
Mechanism
This transition from the State 2: Native/Invaded State to State 4: Invaded State generally occurs with long-term non-use or light grazing, and lack of fire. Exotic cool-season grasses (such as Kentucky bluegrass, smooth brome, crested wheatgrass, and/or annual bromes) become the dominant graminoids.
Studies indicate that a threshold may exist in this transition when both Kentucky bluegrass exceeds 30% of the plant community and native grasses represent less than 40% of the plant community composition. Similar thresholds may exist for other exotic cool-season grasses. This transition may occur under other managerial conditions, including heavy season-long grazing (primarily Kentucky bluegrass).
Context dependence
Variations in growing conditions (e.g., cool, wet spring) will influence effects of various management activities on exotic cool-season grass populations.
Mechanism
This restoration pathway from State 3: Shortgrass State to State 2: Native/Invaded State may be accomplished with a successful grazing land mechanical treatment. Once lesser spikemoss has become well established, mechanical (as well as other) treatments have been largely ineffective in suppressing or eliminating it, even though some short-term reductions may appear successful. As a result, this restoration pathway will likely be temporary.
Context dependence
This community is very resistant to change. Periods of above average precipitation will increase grass and forb production.
Mechanism
This transition from State 3: Shortgrass State to State 4: Invaded State occurs with late season grazing or long-term non-use or light utilization and no fire. Exotic cool-season grasses (such as Kentucky bluegrass, crested wheatgrass, smooth brome, and/or annual bromes) become the dominant graminoids.
Studies indicate that a threshold may exist in this transition when both Kentucky bluegrass exceeds 30% of the plant community and native grasses represent less than 40% of the plant community composition. Similar thresholds may exist for other exotic cool-season grasses. This transition may occur under other managerial conditions, including heavy season-long grazing (primarily Kentucky bluegrass).
Constraints to recovery
Variations in growing conditions (e.g., cool, wet spring) will influence effects of various management activities on exotic
cool-season grass populations.
Mechanism
This restoration pathway from State 4: Invaded State to State 2: Native/Invaded State may be accomplished with the implementation of long-term prescribed grazing and prescribed burning, assuming there is an adequate component of native grasses to respond to the treatments. However, in some cases a subsequent range planting may be necessary to complete the restoration.
Both prescribed grazing and prescribed burning are likely necessary to successfully initiate this restoration pathway, the success of which depends upon the presence of a remnant population of native grasses in Community Phase 4.1. That remnant population, however, may not be readily apparent without close inspection. The application of several prescribed burns may be needed at relatively short intervals in the early phases of this restoration process, in part because many of the shrubs (e.g., western snowberry) sprout profusely following one burn. Early season prescribed burns have been successful; however, fall burning may also be an effective technique.
The prescribed grazing should include adequate recovery periods following each grazing event and stocking levels which match the available resources. If properly implemented, this will shift the competitive advantage from the exotic cool-season grasses to the native cool-season grasses.
Context dependence
Grazing management should be applied in a manner that enhances/maximizes the competitive advantage of native grass and forb species over the exotic species. This may include the use of prescribed grazing to reduce excessive plant litter accumulations above that needed for rangeland health indicator #14 (see Rangeland Health Reference Worksheet). Increasing livestock densities may facilitate the reduction in plant litter provided length and timing of grazing periods are adjusted to favor native species.
Grazing prescriptions designed to address exotic grass invasion and favor native species may involve earlier, short, intense grazing periods with proper deferment to improve native species health and vigor. Fall (e.g., September, October) prescribed burning followed by an intensive, early spring graze period with adequate deferment for native grass recovery may shift the competitive advantage to the native species, facilitating the restoration to State 2: Native/Invaded.
Prescribed burning should be applied in a manner that enhances the competitive advantage of native grass and forb species over the exotic species. Prescribed burns should be applied at a frequency which mimics the natural disturbance regime, or more frequently as is ecologically (e.g., available fuel load) and economically feasible. Burn prescriptions may need adjustment to: (1) account for change in fine fuel orientation (e.g., “flopped” Kentucky bluegrass); (2) fire intensity and duration by adjusting ignition pattern (e.g., backing fires vs head fires); (3) account for plant phenological stages to maximize stress on exotic species while favoring native species (both cool- and warm-season grasses).
Mechanism
This Restoration Pathway from State 5: Go-Back State to the State 2: Native/Invaded State can be accomplished with a successful range planting. Following seeding, long-term prescribed grazing and prescribed burning, haying, or use of herbicides will generally be necessary to achieve the desired result and control any noxious weeds.
It may be possible using selected plant materials and agronomic practices to approach something very near the functioning of State 2: Native/Invaded State. Application of chemical herbicides and the use of mechanical seeding methods using adapted varieties of the dominant native grasses are possible and can be successful. After establishment of the native plant species, prescribed grazing should include adequate recovery periods following each grazing event and stocking levels which match the available resources; management objectives must include the maintenance of those species, the associated reference state functions, and continued treatment of exotic grasses.
Context dependence
A successful range planting will include proper seedbed preparation, weed control (both prior to and after the planting), selection of adapted native species representing functional/structural groups inherent to the State 1, and proper seeding technique. Management (e.g., prescribed grazing, prescribed burning) during and after establishment must be applied in a manner that maintains the competitive advantage for the seeded native species. Adding non-native species can impact the above and below ground biota. Elevated soil nitrogen levels have been shown to benefit smooth brome and Kentucky bluegrass more than some native grasses. As a result, fertilization, exotic legumes in the seeding mix, and other techniques that increase soil nitrogen may promote smooth brome and Kentucky bluegrass invasion.
Excess water not used during or after cropping in adjacent cropland areas may cause increased salinity within the rangeland site. Excess water is usually not attributed to the salinized area but comes from a water recharge site, usually up slope. This water recharge site needs to be determined prior to managing the salinized area. To treat the salinized area (discharge site) excess water (recharge site) needs to be utilized by deep rooted perennial vegetation. Prior to planting the salinized area, determine EC levels and select grass/forb species that are tolerant to the salinity levels. In many cases, water table levels need to be reduced in the salinized area prior to seeding. Seeding the entire area to grass may address water flow (salinization) issue; see NRCS Field Office Technical Guide (FOTG) Standard 550 Range Planting for more information. https://www.nrcs.usda.gov/resources/guides-and-instructions/field-office-technical-guides
The method or methods of herbaceous weed treatment will be site specific to each situation; the goal, generally, would be to apply the pesticide, mechanical control, or biological control (either singularly or in combination) in a manner that shifts the competitive advantage from the targeted species to the native grasses and forbs. The control method(s) should be as specific to the targeted species as possible to minimize impacts to non-target species.
Mechanism
A failed range planting and/or secondary succession will lead to State 4: Invaded State.
Context dependence
Failed range plantings can result from many causes (both singularly and in combination) including drought, poor seedbed preparation, improper seeding methods, seeded species not adapted to the site, insufficient weed control, herbicide carryover, poor seed quality (purity & germination), and/or improper management.
Excess water not used during or after cropping in adjacent cropland areas may cause increased salinity within the rangeland site. Excess water is usually not attributed to the salinized area but comes from a water recharge site, usually up slope. This water recharge site needs to be determined prior to managing the salinized area. To treat the salinized area (discharge site) excess water (recharge site) needs to be utilized by deep rooted perennial vegetation. Prior to planting the salinized area, determine EC levels and select grass/forb species that are tolerant to the salinity levels. In many cases, water table levels need to be reduced in the salinized area prior to seeding. Seeding the entire area to grass may address water flow (salinization) issue; see NRCS Field Office Technical Guide (FOTG) Standard 550 Range Planting for more information. https://www.nrcs.usda.gov/resources/guides-and-instructions/field-office-technical-guides
Mechanism
This transition from any plant community to State 5: Go-Back State. It is commonly associated with the cessation of cropping without the benefit of range planting, resulting in a “go-back” situation. Prolonged periods of recreational activity and concentrated livestock activity are also factors in this transition. Soil conditions can be quite variable on the site, in part due to variations in the management/cropping history (e.g., development of a tillage induced compacted layer (plow pan), erosion, fertility, and/or herbicide/pesticide carryover). Thus, soil conditions should be assessed when considering restoration techniques.
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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.