A common plant in spruce-northern hardwood forests is gold thread, which takes its name from its golden, thin, root-like rhizomes. Native Americans and early settlers used gold thread rhizomes and leaves to dye cloth yellow.
There are several hundred occurrences statewide. A few documented occurrences have good viability and several are protected on public land or private conservation land. This community has a very limited statewide distribution and includes several very large, high quality, old-growth examples. The current trend of this community is probably stable for occurences on public land and private conservation land, or declining slightly elsewhere due to moderate threats related to intensive logging, acid rain deposition, and development pressure.
The number and acreage of spruce-northern hardwood forests in New York have probably declined moderately in recent decades as a result of intensive logging, agriculture, and development.
The number and acreage of spruce-northern hardwood forests in New York have probably declined substantially from historical numbers, likely correlated with past logging, agiculture, and other development.
Threats to forests in general include changes in land use (e.g., clearing for development), forest fragmentation (e.g., roads, intensive logging), and invasive species (e.g., insects, diseases, and plants). Other threats may include over-browsing by deer, fire suppression, and air pollution (e.g., ozone and acidic deposition). Examples of this community that occur at higher elevations (e.g., >3,000 feet) may be more vulnerable to the adverse effects of atmospheric deposition and climate change, especially acid rain and temperature increase. When occurring as expansive forests, the largest threat to the integrity of spruce-northern hardwood forests are activities that fragment the forest into smaller pieces. These activities, such as road building and other development, restrict the movement of species and seeds throughout the entire forest, an effect that often results in loss of those species that require larger blocks of habitat (e.g., black bear, bobcat, certain birds). Additionally, fragmented forests provide decreased benefits to neighboring societies of services these societies often substantially depend on (e.g., clean water, mitigation of floods and droughts, pollination in agricultural fields, and pest control) (Daily et al. 1997). Spruce budworm may be considered a threat to occurrences of spruce-northern hardwood forest that experience extreme outbreaks, especially if it coincides with other stresses and reduces tree regeneration. The spruce budworm (Choristoneura fumiferana) is a native insect that creates canopy gaps in spruce and fir forests of the Eastern United States and Canada. Since 1909, there have been waves of budworm outbreaks throughout the Eastern United States and Canada. The states most often affected are Maine, New Hampshire, New York, Michigan, Minnesota, and Wisconsin (Kucera and Orr 1981). Balsam fir is the is the primary host tree for budworm in the Eastern United States, although white, red, and black spruce are known to be suitable host trees. Spruce budworm may also feed on tamarack, pine, and hemlock. Spruce mixed with balsam fir is more likely to show signs of budworm infestation than spruce in pure stands (Kucera and Orr 1981). Spruce-northern hardwood forests at higher elevations may be threatened by acid rain deposition. The ability of forest soils to resist, or buffer, acidity depends on the thickness and composition of the soil, as well as the type of bedrock beneath the forest floor. Places in the mountainous northeast, like New York's Adirondack and Catskill Mountains, have thin soils with low buffering capacity. Forests in high mountain regions often are exposed to greater amounts of acid than other forests because they tend to be surrounded by acidic clouds and fog that are more acidic than rainfall. When leaves are frequently bathed in this acid fog, essential nutrients in their leaves and needles are stripped away. This loss of nutrients in their foliage makes trees more susceptible to damage by other environmental factors, particularly cold winter weather (US EPA 2005).
Management should focus on activities that help maintain regeneration of the species associated with this community. Deer have been shown to have negative effects on forest understories (Miller et al. 1992, Augustine & French 1998, Knight 2003) and management efforts should strive to ensure that regenerating trees and shrubs are not so heavily browsed that they cannot replace overstory trees when required to do so. Avoid cutting old growth examples and encourage selective logging areas that are under active forestry.
Strive to minimize fragmentation of large forest blocks by focusing development on forest edges, minimizing the width of roads and road corridors extending into forests, and designing cluster developments that minimize the spatial extent of the development. Development projects with the least impact on large forests and all the plants and animals living within these forests are those developments built on brownfields or other previously developed land. These projects have the added benefit of matching sustainable development practices (for example, see: The President's Council on Sustainable Development 1999 final report, US Green Building Council's Leadership in Energy and Environmental Design certification process at http://www.usgbc.org/).
Inventory any remaining large and/or old-growth examples across the state. Continue searching for large sites in good condition (A- to AB-ranked).
Research the composition and collect sufficient plot data for spruce-northern hardwood forests statewide in order to characterize variations and clearly separate this community from spruce flats and balsam flats. Regularly assess the presence and degree of impact that spruce budworm has on this community.
This community is limited to the northern portion of the state and areas of high elevation elsewhere. It is concentrated in the Northern Appalachian Ecoregion of the Adirondack Mountains, where it forms the matrix forest, and Tug Hill Plateau. It is also common in the Saint Lawrence and Lake Champlain Lowlands of the Great Lakes Ecoregion. It is peripheral in the High Allegheny Plateau and Lower New England Ecoregions, where it occurs in small patches, from the Catskill Peaks, Rensselaer Plateau and Northern Taconic Mountains.
This community is suspected to span north to southern Quebec, southwest to the Catskill Mountains of New York, southeast to the Berkshire Mountains of Massachusetts, and northeast to Nova Scotia.
Spruce-northern hardwood forest is a mixed forest that occurs on lower mountain slopes and upper margins of flats on glacial till. This is a broadly defined community with several regional and edaphic variants; it is one of the most common forest types in the Adirondacks. Codominant trees are red spruce (Picea rubens), sugar maple (Acer saccharum), American beech (Fagus grandifolia), yellow birch (Betula alleghaniensis), and red maple (Acer rubrum), with scattered balsam fir (Abies balsamea). Striped maple (Acer pensylvanicum) and mountain maple (A. spicatum) are common subcanopy trees. Characteristic shrubs are hobblebush (Viburnum lantanoides), American fly honeysuckle (Lonicera canadensis), and Canada yew (Taxus canadensis). Characteristic groundlayer plants are common wood-sorrel (Oxalis montana), common wood fern (Dryopteris intermedia), shining fir clubmoss (Huperzia lucidula), wild sarsaparilla (Aralia nudicaulis), bluebeads (Clintonia borealis), goldthread (Coptis trifolia), bunchberry (Cornus canadensis), Canada mayflower (Maianthemum canadense), Indian cucumber-root (Medeola virginiana), and twisted stalk (Streptopus roseus). Characteristic birds include yellow-bellied flycatcher (Empidonax flaviventris), white-throated sparrow (Zonotrichia albicollis), golden-crowned kinglet (Regulus satrapa), pileated woodpecker (Dryocopus pileatus), and gray jay (Perisoreus canadensis) (Edinger et al. 2002).
In the Adirondacks and Catskills the spruce-northern hardwood forests generally occur in the transition zone between lower elevarion beech-maple mesic forests and the higher elevation mountain spruce-fir forests. The spruce trees usually have at least 25% cover and tend to be tall and straighter than the spruce in higher elevation communities that are exposed to wind stress.
Known examples of this community have been found at elevations between 1,340 feet and 3,770 feet.
Several wildflower species of spruce-northern hardwood forests can be observed in bloom throughout the spring and summer. During the spring, flowers of bluebead lily (Clintonia borealis), and Canada mayflower (Maianthemum canadense) appear on the forest floor, followed by bunchberry (Cornus canadensis), goldthread (Coptis trifolia), and wood-sorrel (Oxalis montana).
This New York natural community encompasses all or part of the concept of the following International Vegetation Classification (IVC) natural community associations. These are often described at finer resolution than New York's natural communities. The IVC is developed and maintained by NatureServe.
This New York natural community falls into the following ecological system(s). Ecological systems are often described at a coarser resolution than New York's natural communities and tend to represent clusters of associations found in similar environments. The ecological systems project is developed and maintained by NatureServe.
Acer saccharum (sugar maple)
Betula alleghaniensis (yellow birch)
Betula papyrifera (paper birch)
Fagus grandifolia (American beech)
Picea rubens (red spruce)
Pinus strobus (white pine)
Tsuga canadensis (eastern hemlock)
Acer pensylvanicum (striped maple)
Acer spicatum (mountain maple)
Lonicera canadensis (American fly honeysuckle)
Taxus canadensis (Canada yew, American yew)
Vaccinium myrtilloides (velvet-leaved blueberry)
Viburnum lantanoides (hobblebush)
Aralia nudicaulis (wild sarsaparilla)
Brachyelytrum erectum (southern shorthusk)
Clintonia borealis (blue bead-lily)
Coptis trifolia (gold-thread)
Cornus canadensis (bunchberry)
Dennstaedtia punctilobula (hay-scented fern)
Diphasiastrum digitatum (southern ground-cedar)
Dryopteris carthusiana (spinulose wood fern)
Dryopteris intermedia (evergreen wood fern, fancy wood fern, common wood fern)
Huperzia lucidula (shining firmoss)
Maianthemum canadense (Canada mayflower)
Medeola virginiana (Indian cucumber-root)
Oxalis montana (northern wood sorrel)
Streptopus lanceolatus (rose twisted stalk, rose mandarin)
This figure helps visualize the structure and "look" or "feel" of a typical Spruce-Northern Hardwood Forest. Each bar represents the amount of "coverage" for all the species growing at that height. Because layers overlap (shrubs may grow under trees, for example), the shaded regions can add up to more than 100%.
Augustine, A.J. and L.E. French. 1998. Effects of white-tailed deer on populations of an understory forb in fragmented deciduous forests. Conservation Biology 12:995-1004.
Daily, G.C., S. Alexander, P.R. Ehrlich, L. Goulder, J. Lubchenco, P. Matson, H.A. Mooney, S. Postel, S.H. Schneider, D. Tilman, and G.M. Woodwell. 1997. Ecosystem Services: benefits supplied to human societies by natural ecosystems. Issues In Ecology 2:1-16.
Edinger, G. J., D. J. Evans, S. Gebauer, T. G. Howard, D. M. Hunt, and A. M. Olivero (editors). 2014. Ecological Communities of New York State. Second Edition. A revised and expanded edition of Carol Reschke’s Ecological Communities of New York State. New York Natural Heritage Program, New York State Department of Environmental Conservation, Albany, NY. http://www.dec.ny.gov/docs/wildlife_pdf/ecocomm2014.pdf
Edinger, Gregory J., D.J. Evans, Shane Gebauer, Timothy G. Howard, David M. Hunt, and Adele M. Olivero (editors). 2002. Ecological Communities of New York State. Second Edition. A revised and expanded edition of Carol Reschke's Ecological Communities of New York State. (Draft for review). New York Natural Heritage Program, New York State Department of Environmental Conservation. Albany, NY. 136 pp.
Eyre, F.H., ed. 1980. Forest cover types of the United States and Canada. Society of American Foresters, Washington, D.C.
Heimburger, C.C. 1934. Forest-type studies in the Adirondack Region. Cornell University Experiment Station Memoir 165, Ithaca, New York.
Irland, L.C. 1993. A virgin red spruce and northern hardwoods stand, Maine 1902: its forest management implications. Maine Naturalist 1(4):181-192.
Knight, T.M. 2003. Effects of herbivory and its timing across populations of Trillium grandiflorum (Liliaceae). American Journal of Botany 90:1207-1214.
Kucera, D.R. and P.W. Orr. 1981. Spruce budworm in the eastern United States. Forest Insect and Disease Leaflet 160. U.S. Department of Agriculture, Forest Service, Washington, D.C.
Leopold, Donald J., Carol Reschke, and D.S. Smith. 1988. Old-growth forests of the Adirondack Park, New York. Natural Areas Journal 8: 166-189.
Miller, S.G., S.P. Bratton, and J. Hadidian. 1992. Impacts of white-tailed deer on endangered and threatened vascular plants. Natural Areas Journal 12:67-74.
New York Natural Heritage Program. 2019. New York Natural Heritage Program Databases. Albany, NY.
Reschke, Carol. 1990. Ecological communities of New York State. New York Natural Heritage Program, New York State Department of Environmental Conservation. Latham, NY. 96 pp. plus xi.
Roman, John R. 1980. Vegetation - environment relationships in virgin, middle elevation forests in the Adirondack mountains, New York. Ph.D. thesis. SUNY College of Environmental Science and Forestry. Syracuse, NY. 476 pp.
United States Envoronmental Protection Agency. 2005. Effects of Acid Rain: Forests. Available on line at http:www.epa.gov/airmarkets/acidrain/effects/forests.html Accessed March 2, 2005.
Zon, R. 1914. Balsam fir. Bull. U.S. Department Agriculture No. 55:1-68.
This guide was authored by: Gregory J. Edinger
Information for this guide was last updated on: April 3, 2017
Please cite this page as:
New York Natural Heritage Program. 2019. Online Conservation Guide for Spruce-northern hardwood forest. Available from: https://guides.nynhp.org/spruce-northern-hardwood-forest/. Accessed January 18, 2019.