Non-Forested Wetlands

Non-Forested Wetlands

Taxonomy Machine Name
sector_nonforested_ecosystems
Taxonomy Alias
nonforested_ecosystems
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Humans have altered flood regimes in mesic bottomland forests, which may be exacerbated by climate change.

Submitted by dshannon on

Many mesic bottomland forests have been altered from their original state due to the placement of dams and other water control structures. This has already disrupted natural flood regimes, which will likely be further altered by the direct effects of changes in precipitation and indirect effects of human demands on water during drought periods.

Boxelder may increase in abundance in mesic bottomland forests by the end of the century.

Submitted by dshannon on

The models available are not equipped to capture the complex hydrologic processes that occur in these systems, so actual habitat suitability might differ from what is projected. With that caveat in mind, multiple models models tend to agree that habitat suitability for boxelder may increase. Boxelder is not currently a dominant species in mesic bottomland forests, but may increase in dominance from increased habitat suitability.

American beech and black walnut, common in mesic bottomland forests, are projected to decline in habitat suitability by the end of the century.

Submitted by dshannon on

The models available are not equipped to capture the complex hydrologic processes that occur in these systems, so actual habitat suitability might differ from what is projected. With that caveat in mind, multiple models models tend to agree about the general trajectory of the dominant species in these systems.

Habitat suitability is expected to remain stable for bitternut hickory, sycamore, and white oak in mesic bottomland forests through the end of the century.

Submitted by dshannon on

The models available are not equipped to capture the complex hydrologic processes that occur in these systems, so actual habitat suitability might differ from what is projected. With that caveat in mind, multiple models models tend to agree about the general trajectory of the dominant species in these systems.Some models and scenarios suggest a decrease in habitat suitability or establishment for white oak, but since it is a long-lived species that can tolerate a wide variety of stressors no large changes in white oak are expected over the next several decades.

Habitat suitability is expected to increase for sweetgum and eastern cottonwood by the end of the century, which are common species in mesic bottomland forests.

Submitted by dshannon on

The models available are not equipped to capture the complex hydrologic processes that occur in these systems, so actual habitat suitability might differ from what is projected. With that caveat in mind, multiple models models tend to agree about the general trajectory of the dominant species in these systems.

A projected increase in heavy precipitation in the winter and spring in the coming decades could have a negative impact on mesic bottomland forests.

Submitted by dshannon on

This system is characterized by short, infrequent floods. Extended wet periods could increase both the frequency and duration of flooding, which many species would not be able to tolerate.

A high soil water-holding capacity in many locations might allow mesic upland forests to persist on the landscape.

Submitted by dshannon on

Mesic upland forests tend to have a thick litter layer and high soil organic matter, allowing them to retain moisture. This can help protect them from drying and wildfire during short periods of reduced precipitation.

Some invasive plant species common in mesic upland forests, such as bush honeysuckle and kudzu, may benefit from warmer temperatures.

Submitted by dshannon on

Some models suggest an increase in habitat suitability for kudzu, due to milder winters and a longer growing season. It is hypothesized that nonnative plant species such as these will fill in the gaps created as dominant species decline.