Wet Hardwood Forests
Scenario model
Current ecosystem state
Select a state
Management practices/drivers
Select a transition or restoration pathway
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Transition T1A
Increase in Long Term Hydroperiod
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Transition T1B
Decrease in Long Term Hydroperiod
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Transition T1C
Introduction of Non-Native / Exotic Species
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Transition T1D
Modified for Desired Land Use
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Transition T1E
Human Alteration / Transportation of Materials
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Restoration pathway R2A
Decrease in Long-Term Hydroperiod
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Transition T2A
Introduction of Non-Native / Exotic Species
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Transition T2B
Human Alteration / Transportation of Materials
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Restoration pathway R3A
Increase in Long-Term Hydroperiod
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Transition T3A
Introduction of Non-Native / Exotic Species
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Transition T3B
Modify for Desired Land Use
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Transition T3C
Human Alteration / Transportation of Materials
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Restoration pathway R4A
Removal of Undesirable Species
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Restoration pathway R4B
Removal of Undesirable Species
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Restoration pathway R4C
Removal of Undesirable Species
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Transition T4A
Modify for Desired Land Use
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Transition T4B
Human Alteration / Transportation of Materials
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Restoration pathway R5A
Habitat Restoration
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Restoration pathway R5B
Habitat Restoration
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Restoration pathway R5C
Habitat Restoration
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Transition T5A
Human Alteration / Transportation of Materials
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Restoration pathway T6A
Modified Land Restoration
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No transition or restoration pathway between the selected states has been described
Target ecosystem state
Select a state
Description
Wet Hardwood Forests are evergreen hardwood and/ or palm forests with a variable understory typically dominated by closed canopies of palms and oaks occurring on moist soils, with limestone bedrock often at or very near the surface. These hammocks are subject to flooding from runoff in upland sites and from overflow from adjacent river systems during the wet season.
Characteristics and indicators
Wet hardwood forests are typically low in height, no greater than 80 ft, with a closed canopy and sparse to open understory. Epiphytes are vastly abundant growing on tree trunks and limbs. What species exist in the understory compose of hydrophytic grasses, sedges, and ferns.
Submodel
Description
While wet hardwood forests are tolerant and dependent on occasional flooding to maintain community composition, an increase in long term hydroperiod may shift species vegetation towards more hydrophytic compositions such as a cypress dominated swamp. Increases in long term hydroperiods can occur through anthropogenic alterations such as impoundments or from increases in mean annual precipitation over time.
Submodel
Description
While wet hardwood forests are tolerant and dependent on flooding to maintain community composition, decreases in long term hydroperiod may shift species vegetation towards more mesic and xerophytic compositions. Slight decreases in hydrology in wet hardwood forests is reflected by the presence of drier vegetation such as saw palmetto and live oak. This decreases in long term hydroperiod can occur anthropogenically from drainage and ditching or from extended periods of drought.
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 and can completely replace the native habitat if not properly managed. Restoration to natural communities after exotic non-native invasion includes 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)
5.2. Open Transitional Managed Communities
5.5. 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 an increase in long-term hydrology from natural or anthropogenic means. A viable seedbank must be introduced naturally (aerial dispersal) or anthropogenically (transplanting / seeding) for the growth and success of this transition.
Mechanism
This transition is driven by a decrease in hydrology from natural or anthropogenic means.
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 outcompete and survive in intolerable conditions. Localized knowledge for each species must be known for best management of it it without harming the natural habitat, 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 is driven by a decrease in hydrology from natural or anthropogenic means.
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 outcompete and survive in intolerable conditions. Localized knowledge for each species must be known for best management of it it without harming the natural habitat, 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
This transition is driven by the alteration and/ or transportation of materials via anthropogenic means.
Mechanism
This transition is driven by an increase in hydrology from natural or anthropogenic means.
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 outcompete and survive in intolerable conditions. Localized knowledge for each species must be known for best management of it it without harming the natural habitat, 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 unwanted species through various mechanisms. Localized knowledge for community species composition is needed for specific management. 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 unwanted species is a time dependent process, with removal types taking long times to be considered effective.
Mechanism
Mechanical, biological, and chemical removal strategies include removing the unwanted species through various mechanisms. Localized knowledge for community species composition is needed for specific management. 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 unwanted species is a time dependent process, with removal types taking long times to be considered effective.
Mechanism
Mechanical, biological, and chemical removal strategies include removing the unwanted species through various mechanisms. Localized knowledge for community species composition is needed for specific management. 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 unwanted species is a time dependent process, with 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
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.