Subtropical Moist Hammocks of Miami Ridge / Atlantic Coastal Strip
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
More details -
Transition T1B
Decrease in Long-Term Hydroperiod
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Transition T1C
Invasion of Non-Native / Exotic Species
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Transition T1D
Modify 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
Invasion 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
Increase in Long-Term Hydroperiod
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Transition T3A
Invasion of Non-Native / Exotic Species
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Transition T3B
Modify for Desired Land Use
More details -
Transition T3C
Human Alteration / Transportation of Materials
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Restoration pathway R4A
Mechanical / Biological / Chemical Removal
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Restoration pathway R4B
Mechanical / Biological / Chemical Removal
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Restoration pathway R4C
Mechanical / Biological / Chemical Removal
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Restoration pathway R4D
Mechanical / Biological / Chemical Removal
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Transition T4A
Human Alteration / Transportation of Materials
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Restoration pathway R5A
Landscape and Habitat Restoration
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Restoration pathway R5B
Landscape and Habitat Restoration
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Restoration pathway R5C
Landscape and Habitat Restoration
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Transition T5A
Human Alteration / Transportation of Materials
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No transition or restoration pathway between the selected states has been described
Target ecosystem state
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Description
Moist hammocks are evergreen hardwood and/ or palm forests with a variable understory typically dominated by palms and ferns occurring on moist soils, with limestone bedrock often at or very near the surface. They are characterized by a closed canopy with a dominance of oak species and cabbage palms.
Characteristics and indicators
Moist hammocks 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
This state refers to the alteration of the long term hydroperiod within a moist hammock system. While moist hammocks are tolerant and dependent on flooding to maintain community composition, increases in the long term hydroperiod may shift species vegetation towards more hydrophytic compositions. While slight increases in hydroperiods are seen in moist hammocks, reflected in the presence of hydrophytic vegetation such as cypress, large increases in hydroperiods may change the community altogether.
Submodel
Description
This state refers to the alteration of the long term hydroperiod within a moist hammock system. While moist hammocks are tolerant and dependent on flooding to maintain community composition, decreases in the long term hydroperiod may shift species vegetation towards more mesic and xerophytic compositions. While slight decreases in hydroperiods are seen in moist hammocks, reflected in the presence of mesic and xerophytic vegetation such as pines and saw palmetto, large decreases in hydroperiods may change the community altogether.
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/).
This community will not represent every possibility of invasive species but rather the most common in these areas.
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 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) but are not completely altered by anthropogenic means.
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., Urban land, 0-2% 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 deeply 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 an increase in the long term hydroperiod from natural or anthropogenic means.
Mechanism
This transition is driven by a decrease in the long term hydroperiod 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 changes in natural hydroperiods or 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 frequency or natural hydroperiods 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 transition is driven by a decrease in the long term hydroperiod 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 changes in natural hydroperiods or 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 frequency or natural hydroperiods 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 transition is driven by an increase in the long term hydroperiod 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 changes in natural hydroperiods or 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 frequency or natural hydroperiods 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
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
This transition is driven by the alteration and/ or transportation of materials via anthropogenic means.
Mechanism
These practices include the restoration of both the natural hydroperiods and landscape in advance of revegetating the area (if needed).
Mechanism
These practices include the restoration of both the natural hydroperiods and landscape in advance of revegetating the area (if needed).
Mechanism
These practices include the restoration of both the natural hydroperiods and landscape in advance of revegetating the area (if needed).
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.