Claypan 23-30" PZ
Scenario model
Current ecosystem state
Select a state
Management practices/drivers
Select a transition or restoration pathway
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Transition T1A
Absence of disturbance and natural regeneration over time, may be coupled with excessive grazing pressure
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Transition T1B
Extensive soil disturbance followed by seeding
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Restoration pathway R2A
Adequate rest from defoliation and removal of woody canopy, followed by reintroduction of historic disturbance regimes
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Transition T2A
Extensive soil disturbance followed by seeding
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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 Midgrass Prairie Community (1.1) is the interpretive plant community for the Claypan 23-30” PZ Ecological Site. The site developed as a treeless prairie with few scattered shrubs. Lotebush and ephedra were typical, but infrequent, shrubs. Vine-mesquite occupied favorable micro-sites and was locally dominant. Sideoats grama was the dominant or co-dominant grass throughout the site. Alkali sacaton was prevalent where salt spots occurred in depressions. Blue grama and buffalograss were the most common shortgrasses. Characteristic forbs found on the site include Engelmann daisy, dotted gayfeather, catclaw sensitivebriar, heath aster, western ragweed, and Louisiana sagewort. It is estimated that the Midgrass Prairie Plant Community produced from 1500 to 3000 pounds of biomass annually and that grasses produced as much as 95 percent of the annual production.
The Mixed-grass Prairie Community (1.2) is a mixed midgrass and shortgrass dominated grassland being encroached by indigenous or invading woody species that had been held at low densities by repeated fires and competition from a vigorous grass component. The preferred midgrasses, such as sideoats grama and vine-mesquite, are being replaced by the more grazing resistant grasses such as buffalograss, blue grama and Texas wintergrass. Numerous brushy species, including mesquite and pricklypear, are encroaching because overgrazing by livestock has reduced grass cover, exposed more soil and reduced fine fuel for fire. Mesquite is generally less than three feet tall and still subject to suppression by fire. The woody canopy varies between 5 and 15 percent depending on impact of grazing on herbaceous species, time since burned and availability of invading species. Forage production in the Mixed-grass Prairie Community (1.2) is still predominantly grass. Annual production has declined and averages from 1000 to 2,500 pounds per acre.
Submodel
Description
Shortgrass/Mixed-brush Community (2.1) has a 15 to 35 percent woody plant canopy of mixed-brush. Mesquite is the dominant woody species while pricklypear and lotebush are the most common smaller shrubs. Mesquite is an early increaser throughout the MLRA. Typically, pricklypear, lotebush and tasajillo have also increased in density and frequency in this vegetation type. Remnants of historic climax grasses and forbs and unpalatable invaders occupy the interspaces between trees and shrubs. Cool-season grasses such as Texas wintergrass and annual brome can be found under and around woody plants. Characteristic forbs are heath aster, western ragweed, silverleaf nightshade and annual broomweed. Total plant production declines somewhat, being approximately 900 to 2,300 pounds per acre.
The Mixed-brush/Shortgrass/Annuals Community is a dense shrubland dominated by mesquite. Common understory shrubs are pricklypear, lotebush, and pricklypear. With time and continued heavy grazing and no brush control, the mesquite will become tree-like and approach 75 percent or more canopy cover. Texas wintergrass, shortgrasses and low quality annual and perennial forbs are found under and around the woody species. Characteristic grasses are meadow and sand dropseed, hairy tridens, tumble lovegrass and three-awns. Forbs include heath aster and silverleaf nightshade. Cool-season annuals such Japanese brome and annual broomweed grow profusely during wet springs. Herbaceous plants produce less than 25 percent of the annual production. Total annual production ranges from 800 to 2200 pounds per acre.
Submodel
Description
The Claypan Prairie Ecological Site, with its productive soils, is often cultivated (3.1) and planted to crops. Technical advice as to adapted crops, cropping systems, production, and cultivation practices are available from local NRCS or Extension Service offices. When abandoned from cropping, the site should be re-vegetated with adapted native plant mixtures, which include reference community species.
Submodel
Mechanism
Unless proper grazing and prescribed burning are initiated at this stage, the woody species continue to increase in maturity, size and density and the grassland component declines in density and vigor. When the canopy of the woody plants becomes dense enough (15-20 % canopy) and big enough (greater than four feet) to suppress grass growth and resist fire damage, a threshold in ecological succession is reached. At this threshold the Grassland State transitions into the Shrubland State.
Mechanism
The Grassland State is sometimes converted into a Converted Land State such as cropland and pastureland. Crop cultivation, Plowing, Range Planting, Pasture Planting, Pest Management, Nutrient Management, and Prescribed Grazing are necessary.
Mechanism
With the implementation of brush management, range planting, prescribed grazing, IPT, and prescribed burning, the Woodland State can be restored to the Grassland State.
Relevant conservation practices
Practice | External resources |
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Brush Management |
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Prescribed Burning |
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Prescribed Grazing |
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Range Planting |
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.