Histisol Floodplain Marshes and Swamps
Scenario model
Current ecosystem state
Select a state
Management practices/drivers
Select a transition or restoration pathway
-
Transition T1A
Woody Species Development
More details -
Transition T1B
Invasion of Non-Native / Exotic Species
More details -
Transition T1C
Modify for Desired Land Use
More details -
Transition T1D
Human Alteration / Transportation of Materials
More details -
Restoration pathway R2A
Woody Species Removal
More details -
Transition T2A
Invasion of Non-Native/ Exotic Species
More details -
Transition T2B
Modify for Desired Land Use
More details -
Transition T2C
Human Alteration / Transportation of Materials
More details -
Restoration pathway R3A
Removal of Unwanted Species
More details -
Restoration pathway R3B
Removal of Unwanted Species
More details -
Transition T3A
Modify for Desired Land Use
More details -
Transition T3B
Human Alteration / Transportation of Materials
More details -
Restoration pathway R4A
Landscape and Habitat Restoration
More details -
Restoration pathway R4B
Landscape and Habitat Restoration
More details -
Transition T4A
Human Alteration / Transportation of Materials
More details -
Transition T5A
Modified Land Restoration
More details -
No transition or restoration pathway between the selected states has been described
Target ecosystem state
Select a state
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. Communities closer to the flooding waterbody will have slightly longer hydroperiods than sites found furthest from the flooded waterbody. Shorter hydroperiods are found furthest from the waterbody and are less frequently flooded. They are continuously wet but rarely inundated soils on slightly higher elevations. Relatively longer hydroperiods support more homogenous grassland communities. 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 adjacent to a waterbody that floods.
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, hardwood invasion and peat accumulation create a mixed hardwood and cypress swamp, and under certain conditions the stand may convert to a hardwood forest. Along the floodplain of a river or creek, an even-aged stand of cypress trees may be present throughout. 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. They have smaller, younger trees along the periphery of the swamps furthest from the waterbody contributing to its flooding conditions. These will often form an even-aged stand of cypress trees of relative width and height.
Resilience management
This state is maintained by both stressors from water and fire. Inundation ranges from 100 to 300 days per year which only allow hydrophytic tolerant 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 may be rare in this community, naturally extinguishing itself along the fringes of swamps found adjacent to pyrogenic communities. Interior swamps are very rarely subject to fire due to extreme soil saturation, but is possible during periods of extreme drought, causing peat fires and transitioning the area to a nonforested 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 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 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 soils) 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. The absence of fire can also lead to woody species development by failing to maintain community structure and composition.
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. Due to the extreme wetness of this site, drawdown of the water table may be needed to meet the desirable community.
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 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 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 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
This transition is driven by the alteration and/ or transportation of materials via anthropogenic means.
Model keys
Briefcase
Add ecological sites and Major Land Resource Areas to your briefcase by clicking on the briefcase () icon wherever it occurs. Drag and drop items to reorder. Cookies are used to store briefcase items between browsing sessions. Because of this, the number of items that can be added to your briefcase is limited, and briefcase items added on one device and browser cannot be accessed from another device or browser. Users who do not wish to place cookies on their devices should not use the briefcase tool. Briefcase cookies serve no other purpose than described here and are deleted whenever browsing history is cleared.
Ecological sites
Major Land Resource Areas
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.