Subtropical Freshwater Forested Wetlands of Everglades
Scenario model
Current ecosystem state
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Management practices/drivers
Select a transition or restoration pathway
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Transition T1A
Island Destruction
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Transition T1B
Invasion of Non-Native / Exotic Species
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Transition T1C
Modified for Desired Land Use
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Transition T1D
Human Alteration / Transportation of Materials
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Transition T2A
Organic Matter Accumulation / Woody Species Development
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Restoration pathway R3A
Mechanical / Biological / Chemical Removal of Species
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Transition T3A
Human Alteration / Transportation of Materials
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Restoration pathway R4A
Landscape and Habitat Restoration
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Transition T4A
Human Alteration / Transportation of Materials
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Restoration pathway R5A
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
These occur as isolated areas of mineral soil or organic materials on knolls which support freshwater forested wetland species. These are the "Tree Islands" seen throughout the Everglades that rise above the sawgrass prairies and are subject to frequent flooding conditions during the wet season. They are dominated by a heavy canopy closure, causing deep interior shade, which help control the temperature and moisture retention. The vegetation is dense, heavy, strong wood, and shallow spreading root systems which adapt these species to harsh wind, periodic droughts, fire, and flooding conditions.
It is important to note there are multiple vegetative communities that may exist as tree islands (expressed in the submodel). They are all included in one ESD due to the similar management considerations, flooding frequency, soil components, geomorphic positions, and mapping constraints which may be amended with a higher detail survey in future projects.
Characteristics and indicators
These are the tree islands which rise above the landscape within the Everglades ecoregion. They are generally small in size and orientated in a north south direct in aerial images. During the dry season (November to June) the island may be completely dry and support understory vegetation. During the wet season, the surrounding sawgrass marshes may create flooding conditions which submerge the understory of these islands. These are highly protected communities and hold high cultural importance with the local Native American tribes.
Resilience management
Resilience for these communities is dependent on the specific vegetative community (described in the submodel). However, extended hydroperiods and fire frequency and intensity are the two most important factors in this environment. Extended hydroperiods may cause erosion problems to the mineral islands, destroying this community. Extreme fires may destroy the organic islands, with the absence of fire allowing expansion of the community. Typically once a mineral island is destroyed it cannot be restored, but may be replaced by an organic island (baygall / willow head). Hydrologic management would need to be addressed from the source of flooding, the extensive canals and ditches used to drain the Everglades Agricultural Areas immediately adjacent off the south side of Lake Okeechobee.
Submodel
State 2
Non-Forested Glades Marsh and Slough Wetlands
Description
This state directly correlates with the Non-Forested Glades Marsh and Slough Wetlands Ecological Site and all information regarding this ESD should be referred to in R156AY220FL. This state becomes dominant in replacement of tree islands when they become destroyed. This can be due to hydrologic erosion of mineral soil tree islands by increased hydrologic flow due to human alteration or via destruction from intense fire during drought in the organic soil tree islands.
Characteristics and indicators
These are the sawgrass marsh and slough wetlands that are dominated by vast expanses of sawgrass with open drainageways throughout.
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 introduced to the state by people, weather, or any other means.
Resilience management
This state can be found as a part of any other state 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 removals.
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.
This state may not occupy a large role in this ecological site, but areas in the northern Everglades ecoregion have been extensively altered and managed for range, agriculture, and silviculture in present day uses. Any conversion to these communities have been done over a large landscape setting, primarily the Everglades Agricultural Area. Often the small tree islands will be destroyed and the area will be managed based off the (drained) highly organic soils of the surrounding glades marsh (R156AY220FL).
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)
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., Macks Camp muck, ponded-Urban land complex, 0-2% slopes, occasionally flooded).
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
Transition T1A
Mechanism
This transition is driven by a disturbance which may be natural or anthropogenic, resulting in destruction of the island. Mineral soil tree islands may be lost from anthropogenic activities such as channelization and altering the natural hydroperiod of the landscape, which may permanently flood or erode the mineral soils of the island. Organic islands may be destroyed during periods of drought when fire enters the system and burns the organic material.
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 altered 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 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.
Transition T2A
Mechanism
This transition is only for the formation of organic soil tree islands. Once a mineral soil tree island is destroyed that ecological community is lost, and may only be replaced with organic soil tree islands.
The formation of organic tree islands (specifically ballgalls or willow heads), results from the accumulation of organic matter. Floating mats of organic matter may travel down the drainageways (sloughs) and become stuck, building organic material as sawgrass decomposes over long periods of time. If woody seeds are introduced into the system, this may grow and allow for the development of baygall or willow head.
Context dependence
Note this is a very time depending process and may take hundreds to thousands of year to accumulate organic matter and is dependent on local fire frequency.
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 cutting and removal of invasive species. Chemical removal might include spot spraying 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
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.