Forest [FAR1]

Legacy FAR1 strategy/approaches.

Taxonomy Machine Name
niacs_strategy
Taxonomy Alias
far1

Northern hardwood forests are widely distributed across a variety of sites, increasing adaptive capacity.

Submitted by sdhandler 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 northern hardwoods in the future. In these areas, it is also possible that sites that are currently too wet or cold to support northern hardwoods may become suitable over time and be colonized by these species.

Insect pests and diseases such as beech bark disease and hemlock woolly adelgid could become more problematic in spruce-fir forests under a warmer climate.

Submitted by sdhandler on

Climate change may amplify several major stressors that are already affecting this forest system. Several pests, including beech bark disease and hemlock woolly adelgid, currently affect many forests. Studies suggest that insect pests may increase in northern forests due to increased metabolic activity in active periods and increased winter survival. Insect pests, such as the hemlock woolly adelgid, are expected to cause more frequent and severe damage under climate change. Pests such as Asian longhorned beetle may present new risks as they expand, and new pests present unknown risks.

Projected increases in temperature could lead to additional heat and moisture stress in montane spruce-fir forests.

Submitted by sdhandler on

Lack of snowpack can result in increased risk of shallow roots freezing. Reduced snowfall and snowpack, which lead to earlier spring melt, may also play a large role in soil moisture availability. Fires are rare in this forest community, but extreme drought or tree mortality could increase fire risk.

All dominant species in montane spruce-fir forests are projected to lose habitat and productivity under both climate scenarios, with more substantial impacts projected under greater warming.

Submitted by sdhandler on

Multiple forest impact models tend to agree that northern and boreal conifer species will decrease. Balsam fir and red spruce may not successfully regenerate if moisture is insufficient and average spring or summer temperatures exceed 92 °F. Seedling mortality may also occur during drought or if soil surface temperatures exceed 115 °F.

Montance spruce-fir forests are restricted to the cool, moist environments at the highest elevations in the Mid-Atlantic region.

Submitted by sdhandler on

Protected valleys or coves may continue to provide cool microhabitats where spruce and fir persist. This forest community is projected to lose physical habitat as the climate warms and species migration is limited by complex topography and extreme requirements.