Wet flatwoods are pine forests with a sparse or absent midstory and a dense groundcover of grasses, herbs, and low shrubs. The pine canopy typically consists of one or a combination of longleaf pine, slash pine, pond pine, or South Florida slash pine. This community is found in flatlands with sand substrate and are seasonally inundated. They often occur in the ecotones between mesic flatwoods and shrub bogs, wet prairies, dome swamps, or strand swamps.
Wet flatwoods also occur in broad, low flatlands, often in a mosaic with these communities. The understory and ground cover within this community includes several common species such as saw palmetto, gallberry, wax myrtle, and a wide variety of grasses and herbs, along with fetterbush and bay trees. It is found statewide except extreme southern peninsula and the Keys. Fire occurs fairly frequently, 2-4 years for grassy wet flatwoods and 5-10 years for shrubby wet flatwoods.
This conservation asset includes Hydric Pine Flatwoods, and Hydric Pine Savanna.
Plants within wet flatwoods are already fairly resilient to changes in moisture, having to withstand the stress of soil saturation or inundation during the wet part of the year, as well as dry conditions at other times. However, extreme drought and heat stress caused by increased temperatures could lead to changes in species composition and structure and increased mortality.
For species whose reproductive cycle is linked to wet/dry cycles, changes in the timing and amount of precipitation could affect these life cycle events, potentially causing mismatches of phenological processes, leading to reduced reproductive success, reduced recruitment and increased mortality.
Higher winter air temperatures will increase over-wintering Southern pine beetle larva survival rate, and higher annual air temperatures will allow the beetles to produce more generations per year. Severe drought stress reduces resin production and greatly increases the susceptibility of trees to beetle infestation.
Altered fire regimes or the absence of fire could lead to compositional and structural changes, potentially altering the system's suitability to the current suite of species. The absence of fire in flatwoods communities can lead to a dense mid-story. Additionally, some plants have reduced reproductive success without frequent fire, as fire is required for their reproduction.
Increased summer and winter minimum temperatures, as well as increased extreme events (e.g., droughts, floods) will enhance invasive species processes, from introduction through establishment and expansion.
More information about general climate impacts to habitats in Florida.
Several species, including the frosted flatwoods salamander, reticulated flatwoods salamander and Panama City crayfish, are associated with small wetlands found within a flatwoods matrix. Changes in the timing and amount of precipitation could affect these species' life cycle events, leading to reduced reproductive success, reduced recruitment and increased mortality.
Wet flatwoods provide habitat for large, wide-ranging species such as the Florida panther and black bear. Changes in precipitation and temperature that would lead to fragmentation of these systems would impact the suitability as travel corridors for these species. Species such as the red-cockaded woodpecker and Sherman's fox squirrel would be impacted as the openness of the flatwoods become more densely vegetated as species composition shifts in response to changes in precipitation patterns and altered fire regimes.
More information about general climate impacts to species in Florida.
More information about climate change interactions with existing threats and stressors in Florida.
This habitat was assessed as part of the Standardized Index of Vulnerability and Value Assessment - Natural Communities (SIVVA).
This habitat has a SIVVA vulnerability score greater than 70 but is not among the top 5 most vulnerable natural communities in any SIVVA vulnerability category.
Read more information about SIVVA natural communities.