Histisol Isolated Marshes and Swamps
Scenario model
Current ecosystem state
Select a state
Management practices/drivers
Select a transition or restoration pathway
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Transition T1A
Woody Species Development
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Transition T1B
Introduction of Non-Native / Exotic Species
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Transition T1C
Modify for the Desired Land Use
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Transition T1D
Human Alteration / Transportation of Materials
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Restoration pathway R2A
Woody Species Removal
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Transition T2A
Introduction of Non-Native / Exotic Species
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Transition T2B
Modify for Desired Land Use
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Transition T2C
Human Alteration / Transportation of Materials
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Restoration pathway R3A
Removal of Undesirable Species
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Restoration pathway R3B
Removal of Undesirable Species
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Transition T3A
Modify for Desired Land Use
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Transition T3B
Human Alteration / Transportation of Materials
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Restoration pathway R4A
Landscape and Habitat Restoration
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Restoration pathway R4B
Landscape and Habitat Restoration
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Transition T4A
Human Alteration / Transportation of Materials
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Restoration pathway T5A
Modified Land Restoration
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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 is characterized by a hydroperiod of four to eight months and is typically dominated by hydrophytic grasses and sedges along vast open expanses. Shorter hydroperiods are found in slightly higher elevations and less frequently ponded. They are continuously wet but rarely inundated soils on slightly higher elevations. Longer hydroperiods support more homogenous grassland communities that are inundated more often. The main drivers in this community consist of hydrology and fire regimes, relying on short fire return intervals of 1 to 2 years to maintain its grass and shrub community.
Characteristics and indicators
This state is characterized by large expanses of grasslands and shrublands found on histisols in large depressions that hold standing water for long periods of time.
Submodel
Description
The natural (native) vegetation of this state is mainly dominated by Bald Cypress and Pond Cypress (Taxodium distichum and T. ascendens, respectfully). Occasional fire contributes to the maintenance of a cypress dominated community; without fire, deciduous hardwood invasion and peat accumulation create a mixed hardwood and cypress swamp, and under certain conditions the stand may convert to a hardwood forest. If no adjacent water feature (i.e. rivers), the center of the swamp may contain open marshes or deeper sloughs. These organic soils create a unique environment that increases species diversity and structural development in forested wetland communities.
Characteristics and indicators
This state is characterized by nearly pure stands of cypress trees (Taxodium spp.) that are distinguished by buttressed trunks.
Resilience management
This state is maintained by both stressors from water and fire. Hydroperiods range from 100 to 300 days per year which only allow hydrophytic species to survive. Drainage of this site can allow for the invasion of non-native and exotic species and transition the site to a more mesic hardwood community. Fire is another major stressor in this state, with interior swamps estimated burning at long time periods up to every 100 to 150 years, and the edges every 3 to 5 years. The stress from fire prevents the accumulation of organic matter and transition into a hardwood community.
Submodel
Description
This state consists of Florida Department of Agriculture and Consumer Services (FDACS) Non-Native Category 1 Species list . More information on these species list can be found:
https://www.fdacs.gov/content/download/63140/file/Florida%E2%80%99s_Pest_Plants.pdf
or by contacting the UF / IFAS Center for Aquatic and Invasive Plants (http://plants.ifas.ufl.edu/), the UF / IFAS Assessment of Non-native Plants in Florida's Natural Areas (https://assessment.ifas.ufl.edu/), or the FWC Invasive Plant Management Section (http://myfwc.com/wildlifehabitats/invasive-plants/).
These species are common in areas where natural processes are interrupted via hydrology or fire regimes. The introduction of these species pose serious threats to endangered and threatened habitats and plants within Florida as they become outcompeted for habitats and nutrients.
Characteristics and indicators
Non-Native species include species that exist outside of Florida's natural range and are introduced to the state via people, weather events, or any other means.
Resilience management
This state can be found as a part of any other state or community and can completely destroy the native habitat if not properly managed. Restoration to natural communities after exotic invasion include practices such as mechanical, biological, and chemical removal.
Description
The following communities comprise the major land uses in the United States and the land uses receiving the majority of the conservation treatment that address soil, water, air, plant, and animal resources within the USDA.
Characteristics and indicators
These land uses consist of areas that are not completely naturalized (i.e. native habitat) and have been anthropogenically altered for commodity production.
Submodel
States 2 and 5 (additional transitions)
4.2. Open Transitional Managed Communities
4.5. Silviculture
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 formed 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 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 establishment of woody species. This may be driven naturally or anthropogenically. Natural drivers may be drought, which can lower the water table for an expanded period of time, allowing for hydrophytic species to root and become established. These will often have buttressed trunks as a result of long hydroperiods. Anthropogenic alterations include the drawdown of the water table for commodity products. As the species grow they may shade out the understory and convert the area to a swamp.
Mechanism
The invasion of non-native or exotic species can be driven by a multitude of different environmental factors such as hydrology or changes in fire regimes. Typically once a change in one of the two factors mentioned above occurs, non-native or exotic invasive species become established and begin to compete with native species for habitat and nutrients.
Constraints to recovery
Recovery from non-native or exotic invasive species may be difficult due to many adaptations which allow them to survive and outcompete in intolerable conditions. Localized knowledge for each species must be known for best removal of it without harming the native environment, and often different treatments must be applied over one given area.
Context dependence
Growth of non-native and exotic invasive species can be rapid following a change in a natural stressor such as fire or hydrology which might have once kept the invasive species at bay.
Mechanism
Modify the land for the desired land use. This may include the establishment of grazing species or the modification of land for the cultivation of crops of other desired products.
Mechanism
This transition is driven by the alteration and/ or transportation of materials via anthropogenic means.
Mechanism
This restoration to a grassland from a forest consists of removing the woody species, allowing for light to penetrate the ground surface and grasses in the existing seedbank to grow. This removal may consist of mechanical, biological, or chemical methods to clear an area.
Mechanism
The invasion of non-native or exotic species can be driven by a multitude of different environmental factors such as hydrology or changes in fire regimes. Typically once a change in one of the two factors mentioned above occurs, non-native or exotic invasive species become established and begin to compete with native species for habitat and nutrients.
Constraints to recovery
Recovery from non-native or exotic invasive species may be difficult due to many adaptations which allow them to survive and outcompete in intolerable conditions. Localized knowledge for each species must be known for best removal of it without harming the native environment, and often different treatments must be applied over one given area.
Context dependence
Growth of non-native and exotic invasive species can be rapid following a change in a natural stressor such as fire or hydrology which might have once kept the invasive species at bay.
Mechanism
Modify the land for the desired land use. This may include the establishment of grazing species or the modification of land for the cultivation of crops of other desired products.
Mechanism
This transition is driven by the alteration and/ or transportation of materials via anthropogenic means.
Mechanism
Mechanical, biological, and chemical removal strategies include removing the non-native and exotic invasive species through various mechanisms. Localized knowledge for individual non-native or exotic invasive species is needed for specific management. Sometimes introduction of fire regimes may prevent or stop the growth of non-native or exotic invasive species, but many species are fire tolerant. Mechanical removal might include roller chopping, harvesting, or cutting and removal of invasive species. Chemical removal might include aerial dispersal from planes, or basal bark injection treatments.
Context dependence
Mechanical, biological, and chemical removal of non-native and exotic invasive species is a time dependent process, with both removal types taking long times to be considered effective.
Mechanism
Mechanical, biological, and chemical removal strategies include removing the non-native and exotic invasive species through various mechanisms. Localized knowledge for individual non-native or exotic invasive species is needed for specific management. Sometimes introduction of fire regimes may prevent or stop the growth of non-native or exotic invasive species, but many species are fire tolerant. Mechanical removal might include roller chopping, harvesting, or cutting and removal of invasive species. Chemical removal might include aerial dispersal from planes, or basal bark injection treatments.
Context dependence
Mechanical, biological, and chemical removal of non-native and exotic invasive species is a time dependent process, with both removal types taking long times to be considered effective.
Mechanism
Modify the land for the desired land use. This may include the establishment of grazing species or the modification of land for the cultivation of crops of other desired products.
Mechanism
This transition is driven by the alteration and/ or transportation of materials via anthropogenic means.
Mechanism
These practices include the restoration of both the hydrology and landscape in advance of revegetating the area (if needed).
Mechanism
These practices include the restoration of both the hydrology and landscape in advance of revegetating the area (if needed).
Mechanism
This transition is driven by the alteration and/ or transportation of materials via anthropogenic means.
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.