
Wet Sandy Cutthroat Seeps and Flatwoods
Scenario model
Current ecosystem state
Select a state
Management practices/drivers
Select a transition or restoration pathway
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Transition T1A
Long-Term Fire Suppression / Decrease in Hydroperiod
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Transition T1B
Livestock Introduction / Prescribed Grazing
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Transition T1C
Land Use Conversion / Pasture Development
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Transition T1D
Land Use Conversion / Agricultural Field/ Grove Development
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Transition T1E
Silvicultural Implication and Management
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Transition T1F
Introduction and Establishment of Invasive / Non-Native / Undesirable Species
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Transition T1G
Human Alteration & Human Transportation of Soil Materials
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Restoration pathway R2A
Removal of Undesirable Species / Return to Natural Management Strategies
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Transition T2A
Livestock Introduction / Prescribed Grazing
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Transition T2B
Land Use Conversion / Pasture Development
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Transition T2C
Land Use Conversion / Agricultural Field/ Grove Development
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Transition T2D
Silvicultural Implication and Management
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Transition T2E
Introduction and Establishment of Invasive / Non-Native / Undesirable Species
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Transition T2F
Human Alteration & Human Transportation of Soil Materials
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Restoration pathway R3A
Removal of Livestock / Return to Natural Management Strategies
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Restoration pathway R3B
Removal of Livestock / Return to Natural Management Strategies
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Transition T3A
Land Use Conversion / Pasture Development
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Transition T3B
Land Use Conversion / Agricultural Field/ Grove Development
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Transition T3C
Silvicultural Implication and Management
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Transition T3D
Introduction and Establishment of Invasive / Non-Native / Undesirable Species
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Restoration pathway R4A
Hydrologic Restoration / Return to Natural Management Strategies
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Transition T4A
Land Use Conversion / Agricultural Field/ Grove Development
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Transition T4B
Silvicultural Implication and Management
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Transition T4C
Introduction and Establishment of Invasive / Non-Native / Undesirable Species
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Transition T4D
Human Alteration & Human Transportation of Soil Materials
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Restoration pathway R5A
Hydrologic Restoration / Return to Natural Management Strategies
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Transition T5A
Land Use Conversion / Pasture Development
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Transition T5B
Silvicultural Implication and Management
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Transition T5C
Introduction and Establishment of Invasive / Non-Native / Undesirable Species
More details -
Transition T5D
Human Alteration & Human Transportation of Soil Materials
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Restoration pathway R6A
Selective Timer Removal Activities / Return to Natural Management Strategies
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Restoration pathway R6B
Selective Timer Removal Activities / Return to Natural Management Strategies
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Transition T6A
Introduction and Establishment of Invasive / Non-Native / Undesirable Species
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Transition T6B
Human Alteration & Human Transportation of Soil Materials
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Restoration pathway R7A
Invasion / Non-Native / Undesirable Removal and Restoration
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Restoration pathway R7B
Invasion / Non-Native / Undesirable Removal and Restoration
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Restoration pathway R7C
Invasion / Non-Native / Undesirable Removal and Restoration
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Restoration pathway R7D
Invasion / Non-Native / Undesirable Removal and Restoration
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Restoration pathway R7E
Invasion / Non-Native / Undesirable Removal and Restoration
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Restoration pathway R7F
Invasion / Non-Native / Undesirable Removal and Restoration
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Transition T7A
Human Alteration and / or Human Transportation of Soil Materials
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No transition or restoration pathway between the selected states has been described
Target ecosystem state
Select a state
Description
These are densely vegetated, single-layered grassland communities that are dominated by cutthroat grass (Panicum abscissum). Trees and shrubs are rarely present in its natural state, and will often occur most often along the ecotone of other communities or in an altered state. This community is found along the foot slope toe slope of the Lake Wales Ridge and Bombing Range Ridge, extending exclusively within Polk and Highlands Counties.
Characteristics and indicators
This state is characterized by the stiff, strongly rhizomatous, turf-forming cutthroat grass, which often will result in an overwhelming dominance of this species in each of these communities.
Resilience management
This natural state is maintained by a high water table at or near the surface for most of the year. Cutthroat grass communities exist along the seepage slope and slope break, where groundwater flows downslope and rainfall attribute to the hydric conditions of these communities. These communities are also dependent strongly on frequent fire to maintain community composition and structure. Fire return intervals every 1 to 10 years during the growing season (mid-April to mid-June) should act to prevent extensive woody encroachment.
Submodel
Description
This state is occupied by a open or closed canopy of woody shrubs and trees that have become completely established with the absence of fire from the natural community at one point or another. These are most often created due to alteration of the natural habitat and are the successional climax community of these habitats.
Characteristics and indicators
These areas are characterized by broadleaf evergreen or coniferous wetland shrubs and trees that exist along the side slope and slope breaks of the Lake Wales Ridge and Bombing Range Ridge.
Resilience management
This natural state is maintained by a high water table at or near the surface for most of the year. These communities depend on the absence of fire from the system to allow for woody species to become dominant in the overstory. If fire is reintroduced into the system after pine establishment but before hardwood dominance and is continuously maintained as a fire dependent community it can allow for the creation of a cutthroat flatwoods community. If fire is continuously suppressed it will continue to smother the understory cutthroat grass and can lead to the development of a hardwood dominated baygall.
Submodel
Description
Rangelands are described as lands on which the indigenous vegetation is predominately grasses, grass-like plants, forbs, and possibly shrubs or dispersed trees. Existing plant communities can include both native and introduced plants. Primary export from Florida ranges are cattle and have been present in the state since their first introduction by Spanish explorers in 1521. Native forage production is very good with proper management in this community, with only a slight effect on the community. Proper management will often result in an increase of grasses and reduction of shrubs while also maintaining proper fire intervals.
Rangelands provide a diversity of ecosystems and also provide a diverse and significant production of economic benefits and ecosystem goods and services. Livestock production along with sustainable wildlife populations provide for the major direct economic benefits, but also tourism, recreational uses, minerals/energy production, renewable energy, and other natural resource uses can be very significant. Vital ecosystem contributions include clean water, clean air, fish/wildlife habitat, as well as intangible considerations such as historical, cultural, aesthetic and spiritual values. It is strongly advised that consultation with State Resource Conservationist and District Conservationists at local NRCS Service Centers be sought when assistance is needed in developing management recommendations or prescribed grazing practices.
Submodel
Description
Pasture is a land use type having vegetation cover comprised primarily of introduced or enhanced native forage species that is used for livestock grazing. Pasture vegetation can consist of grasses, legumes, other forbs, shrubs or a mixture. The majority of these forages are introduced, having originally come from areas in other states or continents. Most are now naturalized and are vital components of pasture based grazing systems. Pasture lands provide many benefits other than forage for livestock. Wildlife use pasture as shelter and for food sources. Well managed pasture captures rainwater that slowly infiltrates into the soil which helps recharge groundwater. It is especially important as livestock grazers continues to experience extraordinarily high fuel and other input costs.
Overgrazed pastures can lead to soil compaction and numerous bare spots, which may then become focal points of accelerated erosion and colonization sites of undesirable plants or weeds. It is strongly advised that consultation with State Resource Conservationist and District Conservationists at local NRCS Service Centers be sought when assistance is needed in developing management recommendations or prescribed grazing practices. This grassland / pastureland state correlates with the 2013 Florida Forage Suitability Group G155XB145FL (Sandy Soils on Stream Terraces, Flood Plains or in Depressions).
Submodel
Description
The agriculture industry includes cultivated crops, aquaculture, and apiculture. Cultivated cropland includes areas used for the production of adapted crops for harvest. These areas comprise of land in row crops or close-grown crops that are in a rotation with row or close-grown crops. Primary exports from Florida consist of fruits, greenhouse and nursery products, sugar cane, and the signature export of citrus. Aquaculture includes the cultivation and maintenance of aquatic plants, aquatic reptiles, crustaceans, food/ ornamental fish, shellfish, and other miscellaneous species for harvesting. Apiculture includes the maintenance of honeybees and hives to provide beeswax, honey/ other edible bee products, crop pollination services, and sales of bees to other beekeepers. These areas have been modified resulting in land clearing practices and hydrologic management to fit the growers needs. It is strongly advised that consultation with State Agronomist and District Conservationists at local NRCS Service Centers be sought when assistance is needed in developing management recommendations.
Resilience management
Major natural resource concerns facing cropland include: (1) erosion by wind and water, (2) maintaining and enhancing soil quality, (3) water quality from nutrient and pesticides runoff and leaching, and (4) managing the quantity of water available for irrigation. For more specific information regarding cropland please contact your local NRCS office.
Submodel
Description
This state is important and used by silviculturists, landowners, land managers, and the public/private silviculture industry. The two most common species of trees that can be harvested for timber in this community are slash pine and longleaf pine. Large areas of cutthroat seeps are typically not used for managed woodlands due to the extreme wetness, plant composition, and difficulty of harvest, but may be used for silviculture management if part of a larger wooded area.
Silviculture is land used in controlling the establishment, growth, composition, health, and quality of forests and woodlands to meet the diverse needs and values of landowners and society such as wildlife habitat, timber, water resources, restoration, and recreation on a sustainable basis. These are forestry practices that include thinning, harvesting, planting, pruning, prescribed burning and site preparation, for managed goals such as wildlife habitat creation or harvesting. Many managed silvicultural lands in Florida include tree plantations for growth of tropical ornamental species such as palms; and lumber, pulp, and paper species such as slash pine and longleaf pine.
Resilience management
This state is managed by silviculture prescriptions that will vary based on individual forest stand and management goals.
Submodel
Description
This state represents the dominance of one or multiple non-native or exotic species which outcompetes the native natural community and may significantly alter the composition and structure of the invaded stand by overshading the canopy and understory components and preventing regeneration of native species.
Submodel
Description
These areas include soils that were intentionally and substantially modified by humans for an intended purpose, commonly for terraced agriculture, building support, mining, transportation, and commerce. The alteration is of sufficient magnitude to result in the introduction of a new parent material (human-transported material) or a profound change in the previously existing parent material (human-altered material). They do not include soils modified through standard agricultural practices or farmed soils with unintended wind and water erosion. When a soil is on or above an anthropogenic landform or microfeature, it can be definitely be associated with human activity and is assigned to a unique taxa, usually found as an "Urban land complex" within that communities' natural soil properties (e.g., Immokalee sand-Urban land complex, 0 to 2 percent slopes).
Characteristics and indicators
Evidence of these areas include soils with manufactured items (e.g. artifacts) present in the profile, human altered-materials (e.g., deeply excavated or plowed soil) or human-transported material (e.g., fill), and position on or above anthropogenic landforms (e.g., flood-control levees) and microfeatures (e.g., drainage ditches). Detailed criteria regarding the identification of anthropogenic (artificial) landforms, human-altered materials, and human-transported material are in the "Keys to Soil Taxonomy" (Soil Survey Staff, 2014).
Submodel
Mechanism
This transition is driven by the long-term absence of fire from these communities. Fire suppression for 10 to 40 years. This long-term fire-suppression allows the growth of shrub and tree species present from short-term suppressed areas out of the understory into the overstory. This will shade out the understory that was once dominant by dense cutthroat grass. Absence of fire may be due to increased fragmentation of natural habitats and mismanagement of natural communities.
Constraints to recovery
Once the shrub and trees become established, mechanical, biological, and/or chemical removal of species will be required to return to the reference state.
Context dependence
Long-term fire-suppression from 10 to 40 years will allow for the establishment of immature shrub and tree layer to become established and closely to completely shade the understory. This will remove the cutthroat grass as a dominant understory species.
Mechanism
This mechanism is driven by the introduction of livestock species to the natural system and implementing a planned grazing strategy. Use of a planned grazing strategy to balance animal forage demand with available forage resources. Timing, duration, and frequency of grazing are controlled and some type of grazing rotation is applied to allow for plant recovery following grazing.
Constraints to recovery
It is strongly advised that consultation with State Resource Conservationist and District Conservationists at local NRCS Service Centers be sought when assistance is needed in developing management recommendations or prescribed grazing practices.
Mechanism
Actions required to convert native habitat to pasture or forage production include herbicide application, seedbed preparation, and the establishment of desired plants. Decisions to convert native land to pastureland on this site should be made carefully and continuously evaluated before, during, and after conversion activities. This site is extremely susceptible to soil compaction and erosion. The decision to proceed with this action should be done so in close communication with and guidance from local NRCS Service Centers.
Constraints to recovery
Under natural conditions these areas are identified as wetlands. Altering the natural conditions to create proper drainage for agricultural needs should be carefully managed and assessed during, before, and after conversions.
Mechanism
Actions required to convert native habitat to agricultural land include herbicide application, seedbed preparation, and the establishment of desired plants. Decisions to convert native land to agriculture on this site should be made carefully and continuously evaluated before, during, and after conversion activities. This site is extremely susceptible to soil compaction and erosion. The decision to proceed with this action should be done so in close communication with and guidance from local NRCS Service Centers.
Constraints to recovery
Under natural conditions these areas are identified as wetlands. Altering the natural conditions to create proper drainage for agricultural needs should be carefully managed and assessed during, before, and after conversions.
Mechanism
This pathway consists of prescribed silvicultural activities specifically designed to meet stand compositional and production objectives. For increasing native pine recruitment and production (State 6 Phase 1- Slash Pine (Pinus elliottii) / South Florida Slash Pine (Pinus elliottii var. densa) Managed Stand) achieving proper pine regeneration and maintenance is necessary. Low intensity ground fires and shelter/ seed tree management may assist in creating natural regeneration while promoting a healthy understory system. For management of more well drained pine species (State 7 Phase 2- Longleaf Pine (Pinus palustris) Managed Stand) alteration of the natural habitat may be required to create suitable conditions or may have been a result of past land use alteration (bedding, ditching) while utilizing low intensity ground fires and shelter/ seed tree management for necessary growth.
Constraints to recovery
It is strongly advised that consultation with State Resource Conservationist and District Conservationists at local NRCS Service Centers be sought when assistance is needed in developing management recommendations or prescribed silvicultural practices.
Mechanism
This transition represents proliferation and dominance of an invasive species. Soil mechanical disturbances can compound this effect and create suitable conditions for invasive species.
Mechanism
This transition is driven by the alteration and/ or transportation of materials via anthropogenic means.
Mechanism
This restoration strategy includes the removal of the undesirable woody species through mechanical, biological, and / or chemical means to assist in its return to a natural state. This should incorporate sensitive, non-invasive practices that favors reestablishment of cutthroat grass while minimizes soil disturbance. Once overstory species have been removed a fire return interval mimicking the natural return interval of every 1 to 3 years should be reintroduced during the growing season to promote the flowering and growth of cutthroat grass.
Context dependence
Initial removal of trees in these communities may be necessary to restore areas where trees have shaded out herbaceous vegetation. This may be accomplished via hand cutting or the use of stem-selective herbicides. Large scale mechanical site preparation such as roller chopping or discing should not be used in these areas.
Fire intervals should mimic the natural return interval of every 1 to 3 years during the growing season to promote flowering and growth of cutthroat grass. This should be implemented continuously over the long-term to prevent woody reestablishment.
Mechanism
This mechanism is driven by the introduction of livestock species to the natural system and implementing a planned grazing strategy. Use of a planned grazing strategy to balance animal forage demand with available forage resources. Timing, duration, and frequency of grazing are controlled and some type of grazing rotation is applied to allow for plant recovery following grazing.
Constraints to recovery
It is strongly advised that consultation with State Resource Conservationist and District Conservationists at local NRCS Service Centers be sought when assistance is needed in developing management recommendations or prescribed grazing practices.
Mechanism
Actions required to convert woodlands to pasture or forage production include forest clearing, stump removal, herbicide application, seedbed preparation, and the establishment of desired plants. Decisions to convert woodlands to pastureland on this site should be made carefully and continuously evaluated before, during, and after conversion activities. This site is extremely susceptible to soil compaction and erosion. The decision to proceed with this action should be done so in close communication with and guidance from local NRCS Service Centers.
Mechanism
Actions required to convert native habitat to agricultural land include herbicide application, seedbed preparation, and the establishment of desired plants. Decisions to convert native land to agriculture on this site should be made carefully and continuously evaluated before, during, and after conversion activities. This site is extremely susceptible to soil compaction and erosion. The decision to proceed with this action should be done so in close communication with and guidance from local NRCS Service Centers.
Constraints to recovery
Under natural conditions these areas are identified as wetlands. Altering the natural conditions to create proper drainage for agricultural needs should be carefully managed and assessed during, before, and after conversions.
Mechanism
This pathway consists of prescribed silvicultural activities specifically designed to meet stand compositional and production objectives. For increasing native pine recruitment and production (State 6 Phase 1- Slash Pine (Pinus elliottii) / South Florida Slash Pine (Pinus elliottii var. densa) Managed Stand) achieving proper pine regeneration and maintenance is necessary. Low intensity ground fires and shelter/ seed tree management may assist in creating natural regeneration while promoting a healthy understory system. For management of more well drained pine species (State 7 Phase 2- Longleaf Pine (Pinus palustris) Managed Stand) alteration of the natural habitat may be required to create suitable conditions or may have been a result of past land use alteration (bedding, ditching) while utilizing low intensity ground fires and shelter/ seed tree management for necessary growth.
Constraints to recovery
It is strongly advised that consultation with State Resource Conservationist and District Conservationists at local NRCS Service Centers be sought when assistance is needed in developing management recommendations or prescribed silvicultural practices.
Mechanism
This transition represents proliferation and dominance of an invasive species. Soil mechanical disturbances can compound this effect and create suitable conditions for invasive species.
Mechanism
This transition is driven by the alteration and/ or transportation of materials via anthropogenic means.
Mechanism
This mechanism is driven by the removal of livestock species from the naturally grazed system and restoring natural frequent fire intervals to maintain natural community composition and structure.
Mechanism
This mechanism is driven by the removal of livestock species from the naturally grazed system and restoring natural frequent fire intervals to maintain natural community composition and structure.
Mechanism
Actions required to convert rangeland to pasture or forage production include forest clearing, stump removal, herbicide application, seedbed preparation, and the establishment of desired plants. Decisions to convert woodlands to pastureland on this site should be made carefully and continuously evaluated before, during, and after conversion activities. This site is extremely susceptible to soil compaction and erosion. The decision to proceed with this action should be done so in close communication with and guidance from local NRCS Service Centers.
Mechanism
Actions required to convert native habitat to agricultural land include herbicide application, seedbed preparation, and the establishment of desired plants. Decisions to convert native land to agriculture on this site should be made carefully and continuously evaluated before, during, and after conversion activities. This site is extremely susceptible to soil compaction and erosion. The decision to proceed with this action should be done so in close communication with and guidance from local NRCS Service Centers.
Mechanism
This pathway consists of prescribed silvicultural activities specifically designed to meet stand compositional and production objectives. Decisions to convert land to silviculture on this site should be made carefully and continuously evaluated before, during, and after conversion activities. This pathway consists of prescribed silvicultural activities specifically designed to meet stand compositional and production objectives.
Mechanism
This transition represents proliferation and dominance of an invasive species. Soil mechanical disturbances can compound this effect and create suitable conditions for invasive species.
Mechanism
This mechanism is driven by restoring natural hydrologic flow to the area (dependent on level of alteration) to meet the natural hydroperiod once supported by these communities. This can be done via blocking or filling in previously made ditches used to drain and channelize water flow out of the system from pasture or other land use management. Other management practices such as replanting native grasses (cutthroat grass) and prescribed burning must be implemented to return the to the natural state. Local site conditions and disturbances may determine existing plant seed banks and community composition of managed grasslands/ pastures. Frequent fires should be implemented every 1 to 3 years in the growing season (April to mid-June) to help promote flowering native species while controlling invasive plants and encroaching woody shrubs and trees. The decision to proceed with this action should be done so in close communication with and guidance from local NRCS Service Centers.
Mechanism
Actions required to convert native habitat to agricultural land include herbicide application, seedbed preparation, and the establishment of desired plants. Decisions to convert native land to agriculture on this site should be made carefully and continuously evaluated before, during, and after conversion activities. This site is extremely susceptible to soil compaction and erosion. The decision to proceed with this action should be done so in close communication with and guidance from local NRCS Service Centers.
Mechanism
This pathway consists of prescribed silvicultural activities specifically designed to meet stand compositional and production objectives. Decisions to convert land to silviculture on this site should be made carefully and continuously evaluated before, during, and after conversion activities. This pathway consists of prescribed silvicultural activities specifically designed to meet stand compositional and production objectives.
Mechanism
This transition represents proliferation and dominance of an invasive species. Soil mechanical disturbances can compound this effect and create suitable conditions for invasive species.
Mechanism
This transition is driven by the alteration and/ or transportation of materials via anthropogenic means.
Mechanism
This mechanism is driven by restoring natural hydrologic flow to the area (dependent on level of alteration) to meet the natural hydroperiod once supported by these communities. This can be done via blocking or filling in previously made ditches used to drain and channelize water flow out of the system from pasture or other land use management. Other management practices such as replanting native grasses (cutthroat grass) and prescribed burning must be implemented to return the to the natural state. Local site conditions and disturbances may determine existing plant seed banks and community composition of managed grasslands/ pastures. Frequent fires should be implemented every 1 to 3 years in the growing season (April to mid-June) to help promote flowering native species while controlling invasive plants and encroaching woody shrubs and trees. The decision to proceed with this action should be done so in close communication with and guidance from local NRCS Service Centers.
Mechanism
Actions required to convert agriculture to pasture or forage production include forest clearing, stump removal, herbicide application, seedbed preparation, and the establishment of desired plants. Decisions to convert woodlands to pastureland on this site should be made carefully and continuously evaluated before, during, and after conversion activities. This site is extremely susceptible to soil compaction and erosion. The decision to proceed with this action should be done so in close communication with and guidance from local NRCS Service Centers.
Mechanism
This pathway consists of prescribed silvicultural activities specifically designed to meet stand compositional and production objectives. Decisions to convert land to silviculture on this site should be made carefully and continuously evaluated before, during, and after conversion activities. This pathway consists of prescribed silvicultural activities specifically designed to meet stand compositional and production objectives.
Mechanism
This transition represents proliferation and dominance of an invasive species. Soil mechanical disturbances can compound this effect and create suitable conditions for invasive species.
Mechanism
This transition is driven by the alteration and/ or transportation of materials via anthropogenic means.
Mechanism
Very selective time removal activities should be conducted to restore cutthroat seeps from a timber managed state. Timber removal should only be done in the winter months, when there is very little to no water present at the soil surface, and in a way that favors maintenance of indigenous ground cover vegetation and minimizes soil disruption. Only use skidders with large, soft tires, and only log in the driest weather to prevent rutting and compaction. Avoid dragging log butts or ends in the ground to minimize soil disturbances. Leave trees should be avoided to prevent damage when removing selective species, avoid leaving slash pines and locate landing zones outside of sensitive habitats.
Once proper removal of selective timber activities are completed, restored maintenance of the natural community is needed to control desired community structure and composition.
Context dependence
Timber removal activities should be carefully managed to prevent damage to the natural community. The effects of logging on ground cover must be assessed after each individual logging event. Frequent fires should be reintroduced (if excluded during silviculture management) every 1 to 3 years during the growing season to promote flowering and seeding of natural grasses while preventing woody species encroachment.
Mechanism
Very selective time removal activities should be conducted to restore cutthroat seeps from a timber managed state. Timber removal should only be done in the winter months, when there is very little to no water present at the soil surface, and in a way that favors maintenance of indigenous ground cover vegetation and minimizes soil disruption. Only use skidders with large, soft tires, and only log in the driest weather to prevent rutting and compaction. Avoid dragging log butts or ends in the ground to minimize soil disturbances. Leave trees (if present/ applicable) should be avoided to prevent damage when removing selective species, avoid leaving slash pines and locate landing zones outside of sensitive habitats.
Once proper removal of selective timber activities are completed, restored maintenance of the natural community is needed to control desired community structure and composition.
Context dependence
Timber removal activities should be carefully managed to prevent damage to the natural community. The effects of logging on ground cover must be assessed after each individual logging event. Restoration to the Cutthroat Woodland state should be managed to meet the Cutthroat Flatwoods community (Phase 2.2), in which cutthroat grass is present with the overstory of pine. Frequent fires should be reintroduced (if excluded during silviculture management) every 1 to 3 years during the growing season to promote flowering and seeding of natural grasses while preventing woody species encroachment.
Mechanism
This transition represents proliferation and dominance of an invasive species. Soil mechanical disturbances can compound this effect and create suitable conditions for invasive species.
Mechanism
This transition is driven by the alteration and/ or transportation of materials via anthropogenic means.
Mechanism
The establishment of, or a return to, natural habitat conditions following a previous invasive / non-native / undesirable species infestation may be possible in some areas. Successful actions will require relentless efforts that include removal of the species via chemical, mechanical, and / or biological means. In some extreme cases, restoration attempts could result in greater erosion and worsening of local conditions. Please consult with District and Soil Conservationists at local NRCS Field Offices for advice and guidance on land restoration attempts on invaded areas.
Mechanism
The establishment of, or a return to, natural habitat conditions following a previous invasive / non-native / undesirable species infestation may be possible in some areas. Successful actions will require relentless efforts that include removal of the species via chemical, mechanical, and / or biological means. In some extreme cases, restoration attempts could result in greater erosion and worsening of local conditions. Please consult with District and Soil Conservationists at local NRCS Field Offices for advice and guidance on land restoration attempts on invaded areas.
Mechanism
The establishment of, or a return to, altered land use conditions following a previous invasive / non-native / undesirable species infestation may be possible in some areas. Successful actions will require relentless efforts that include removal of the species via chemical or mechanical or biological means. In some extreme cases, restoration attempts could result in greater erosion and worsening of local conditions. Please consult with District and Soil Conservationists at local NRCS Field Offices for advice and guidance on land restoration attempts on invaded areas.
Mechanism
The establishment of, or a return to, altered land use conditions following a previous invasive / non-native / undesirable species infestation may be possible in some areas. Successful actions will require relentless efforts that include removal of the species via chemical or mechanical or biological means. In some extreme cases, restoration attempts could result in greater erosion and worsening of local conditions. Please consult with District and Soil Conservationists at local NRCS Field Offices for advice and guidance on land restoration attempts on invaded areas.
Mechanism
The establishment of, or a return to, altered land use conditions following a previous invasive / non-native / undesirable species infestation may be possible in some areas. Successful actions will require relentless efforts that include removal of the species via chemical or mechanical or biological means. In some extreme cases, restoration attempts could result in greater erosion and worsening of local conditions. Please consult with District and Soil Conservationists at local NRCS Field Offices for advice and guidance on land restoration attempts on invaded areas.
Mechanism
The establishment of, or a return to, altered land use conditions following a previous invasive / non-native / undesirable species infestation may be possible in some areas. Successful actions will require relentless efforts that include removal of the species via chemical or mechanical or biological means. In some extreme cases, restoration attempts could result in greater erosion and worsening of local conditions. Please consult with District and Soil Conservationists at local NRCS Field Offices for advice and guidance on land restoration attempts on invaded areas.
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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.