Non-Forested Wetlands

Non-Forested Wetlands

Taxonomy Machine Name
sector_nonforested_ecosystems
Taxonomy Alias
nonforested_ecosystems
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Most dominant tree species in northern hardwood forests in Michigan are expected to tolerate a mild amount of warming, but many species could deline under a warmer, drier climate by the end of the century.

Submitted by sdhandler on

Models projections are mixed for many common species that make up northern hardwood forests in Michigan. American basswood, American beech, black cherry, eastern white pine, green ash, northern red oak, red maple, and sugar maple are generally projected to increase under mild climate scenarios, but these species are more likely to decrease under hotter, drier conditions. Deciduous forest systems may be more able to increase productivity across a range of climate scenarios than coniferous forest systems.

Northern hardwood forests may be susceptible to increased drought and moisture stress due to climate change.

Submitted by sdhandler on

Climate projections and forest ecosystem models suggest that forest ecosystems may become more water-limited under climate change, due to longer and warmer growing seasons, precipitation changes, earlier snowmelt. Hardwoods on moist, rich soils may be buffered from short-term droughts or seasonal moisture stress, but these forests may suffer on marginal soils. Increased CO2 concentrations may also increase the water-use efficiency of some species, reducing the risk of moisture stress.

Insect pests like forest tent caterpillar and spongy moth (Lymantria dispar) and diseases like hypoxylon canker may become more active and damaging in aspen-birch forests under a warmer climate.

Submitted by sdhandler on

Under a high emissions scenario, researchers forecast more insect pest damage in northern forests due to increased metabolic activity in active periods and increased winter survival. Drought-stressed trees are also typically more vulnerable to insect pests and diseases. The possibility exists for interactions among multiple stressors to lead to more severe climate change impacts.

Model projections for aspen are mixed under a range of future climate scenarios across northern Michigan, but drought stress may contribute to future declines.

Submitted by sdhandler on

Quaking aspen and bigtooth aspen can tolerate a wide range of soil types and moisture conditions and aspen is a management priority for many landowners. These species may do well with a moderate amount of future warming, and the Tree Atlas and LANDIS models project either no change or slight increases for quaking aspen and bigtooth aspen by the end of the century under the mildest future climate scenario. Both models indicate that these species will fare much worse under hotter, drier climate scenarios.

Many dominant tree species in aspen-birch forests are expected to decline across northern Michigan by the end of the century (quaking aspen, balsam poplar, and paper birch).

Submitted by sdhandler on

Quaking aspen, balsam poplar, and paper birch are boreal species near their southern range limits in Michigan. 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. These species exist on a wide range of soils and landforms, and this forest type is a management priority for many landowners.

Aspen-birch forests may be tolerant of increased disturbance to climate change.

Submitted by sdhandler on

Aspen and paper birch are pioneer species evolved to thrive with regular disturbance. Wildfire and blowdown events could become more common under climate change, and continued management could benefit this forest type, but it is unknown whether aspen-birch forests would continue to persist if stand-replacing disturbances become much more frequent.

Aspen-birch forests may be vulnerable to temperature increases and moisture stress from climate change.

Submitted by sdhandler on

If climate change results in increased moisture stress during the growing season, drier sites will be exposed to greater drought stress and mortality. Warmer growing-season temperatures might encourage more suckering after disturbance, but projected temperatures in the assessment area may be beyond the physiological limits of aspen and birch species.

Lowland conifer forests may not be able to migrate to other locations on the landscape to cope with climate change.

Submitted by sdhandler on

Lowland conifer forests are not expected to expand to new territory or outcompete other forest types, but acid or alkaline soil conditions may make them less suitable for invasive species or competing forest types.

Most dominant tree species in lowland conifer forests are expected to decline across northern Michigan by the end of the century (balsam fir, black spruce, eastern hemlock, northern white-cedar, and tamarack).

Submitted by sdhandler on

These are boreal species near their southern range limits in Michigan. 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. These forests may not maintain their identity if dominant species decline and water tables change.