Forest

FAR2

Taxonomy Machine Name
niacs_strategy_far2
Taxonomy Alias
far2

Many of the dominant tree species are projected to have similar or increased habitat, including American elm, eastern cottonwood, and silver maple.

Submitted by Maria on

This forest system contains many tree species that are tolerant of warmer temperatures and are located in the central to northern portion of their range in New England and northern New York. Multiple forest impact models tend to agree that these species are likely to increase in suitable habitat and biomass across a range of climate scenarios by the end of the century. Species such as American elm, eastern cottonwood, and silver maple are expected to gain suitable habitat across the assessment area under a range of climate futures.

Many tree species could tolerate limited increases in flooding and drought under climate change.

Submitted by Maria on

Many species in riparian and lowland forests can tolerate intermittent wet and dry conditions, and
they can tolerate periodic floods and moisture stress. Extended droughts would cause significant damage
to shallow-rooted species, but increased winter and spring precipitation could buffer summer droughts
in low-lying areas on the landscape.

Lowland and riparian forests may have limited tolerance to changes in precipitation and water tables.

Submitted by Maria on

Climate change has the potential to substantially alter the hydrologic regimes in lowland and riparian systems. These hardwood forests are adapted to annual and seasonal water table fluctuations; however, more intense and variable precipitation events may present risks to this system through excessive flooding, inundation, streambank erosion, or prolonged droughts between heavy precipitation events. Extended droughts could cause significant damage to shallow-rooted species, but increased winter and spring precipitation may buffer summer droughts in low-lying areas on the landscape.

Many of the dominant tree species are expected to decline by the end of the century, including black spruce, red spruce, northern-white cedar and balsam fir.

Submitted by Maria on

These are northern species near their southern range limits in New England and northern New York. Multiple forest impact models tend to agree that these species are more likely to decline in suitable habitat and biomass across a range of climate scenarios by the end of the century. Impacts from climate change are projected to be less severe in the northern part of the assessment area, such as in Maine, allowing the dominant species to persist in some areas.

Changes in herbivore populations may also have substantial effects on forest growth and composition, especially in regard to northern-white cedar.

Submitted by Maria on

Changes in snowfall amount and duration throughout the assessment area may change the wintertime foraging behavior for herbivores such as moose, white-tailed deer, and snowshoe hare. Moose are expected to be negatively affected by numerous changes in the future, including heat stress and increased parasitism from winter ticks. In contrast, deer may benefit in many parts of the region as warmer winter temperatures and reduced snow depth increase access to winter forage.

Organic soils may be more vulnerable to change in lowland mixed conifer forests.

Submitted by Maria on

Sphagnum moss, the primary source of peat in these systems, may be susceptible to warmer conditions. Warmer growing seasons may increase evapotranspiration rates and reduce the rate of peat accumulation in these forests, and peat layers may begin to erode as decomposition rates increase.

Lowland conifer forests may have limited tolerance to changes in precipitation and water tables.

Submitted by Maria on

Lowland conifer forests function in a relatively narrow window of hydrologic and soil conditions. These conditions are expected to be perturbed in a variety of ways, including through increased severe precipitation events and flooding, increased risk of drought, and changes in the water table or relative influence of precipitation versus groundwater. In general, drier conditions would be expected to have a greater negative impact than excess moisture. Organic soils could decompose more quickly under warmer and drier conditions.

Low-elevation spruce-fir forests are widely distributed across a variety of sites, increasing adaptive capacity.

Submitted by Maria on

These forests are also prevalent across the region on a wide variety of soils and landforms. Not all areas are expected to be affected equally, and in general, areas that are north-facing, at higher elevations, or are farther north in the region are expected to undergo less change and may continue to support spruce-fir forest in the future. At the same time, spruce-fir forests that are farther south may have a reduced capacity to cope with future conditions, particularly where past land use or management has already impaired the system.

Low species diversity may reduce the ability of forests to adapt to climate change.

Submitted by Maria on

These forests tend to have relatively low diversity and be dominated by a relatively small number of northern and boreal species. Forests with lower species diversity may be more vulnerable. Further, management often favors the hardwood component in these forests, and additional stress or disturbance may continue to shift forest composition toward hardwood species.

Some tree species may be more likley to persist or become more competative through the end of the century , including white pine, red maple, and some northern hardwood species.

Submitted by Maria on

These species all tolerate a fairly wide range of conditions. Multiple forest impact models tend to agree that these species are more likely to increase or remain stable in suitable habitat and biomass under a mild climate scenario, but these species may fare worse under a hotter, drier future climate scenario.