Ecological dynamics
[Caveat: The vegetation information contained in this section and is only provisional, based on concepts, and future projects support validation through field work. *] The vegetation groupings described in this section are based on the terrestrial ecological system classification and vegetation associations developed by NatureServe (Comer 2003) and localized associations provided by the New York Natural Heritage Program (Edinger et al. 2014).
This site is dominated by red spruce, sometimes mixed with black spruce, and a sphagnum moss understory. It is often logged, which sets the stand through a series of phases, beginning with herbaceous colonizers, then dense spruce and balsam fir saplings, and eventually to mature spruce-fir forest. Within 100 years, any balsam fir dies out from the overstory, and red spruce once again dominates the site. Similar community dynamics occur within stands on this site as blowdowns or spruce budworm open up small patches of mature overstory trees for establishment by herbs and conifer saplings. Large-scale budworm outbreaks are expected to have result in similar dynamics as large-scale timber harvest.
In some areas this site has been converted to perennial grass hayland.
State 1
Reference State (minimally-managed)
This site occurs in gently sloping areas near the bottom of watersheds where water saturates glacial till deposits for much of the growing season. Soils are poorly-drained with varying textures and parent materials. The water table is seasonally high (within 18 inches of the surface) and typically dries out in late summer and fall. This site is typically drier than Loamy Till Seepage Bottoms (Cedar), is not usually ponded, and does not include a major component of very poorly-drained soils. Black spruce and red spruce are abundant, with larch common and balsam fir occurring in younger patches. Cinnamon fern and other herbs are often abundant in the understory.
Resilience management. This site is dominated by red spruce, sometimes mixed with black spruce, and a sphagnum moss understory. It is often logged, which sets the stand through a series of phases, beginning with herbaceous colonizers, then dense spruce and balsam fir saplings, and eventually to mature spruce-fir forest. Within 100 years, any balsam fir dies out from the overstory, and red spruce once again dominates the site. Blowdowns with subsequent gap regeneration are the most frequent form of natural disturbance, with large-scale fires important at longer return intervals.
Dominant resource concerns
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Ponding and flooding
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Plant productivity and health
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Plant structure and composition
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Plant pest pressure
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Wildfire hazard from biomass accumulation
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Terrestrial habitat for wildlife and invertebrates
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Aquatic habitat for fish and other organisms
Community 1.1
Spruce - Northern Hardwood Forest
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), blue bead-lily (Clintonia borealis), goldthread (Coptis trifolia), bunchberry (Cornus canadensis), Canada mayflower (Maianthemum canadense), Indian cucumber-root (Medeola virginiana), and twisted stalk (Streptopus roseus).
(Edinger et al. 2014)
Resilience management. New York Natural Heritage Program State Rank: S3/S4
S3- Typically 21 to 100 occurrences, limited acreage, or miles of stream in New York State.
S4- Apparently secure in New York State.
Gaps formed by wind, snow, ice, and harvesting are the major replacement agents; fires may be important but only over a long return interval.
(Edinger et al. 2014)
Dominant resource concerns
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Ponding and flooding
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Plant productivity and health
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Plant structure and composition
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Plant pest pressure
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Wildfire hazard from biomass accumulation
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Terrestrial habitat for wildlife and invertebrates
State 2
Semi-natural State
Shifts in ecological site composition, functionality, and dynamics driven by natural disturbances, processes, and pressures (may have some anthropogenic drivers). More research is needed to determine the extent of the Semi-natural state associated with this ecological site.
Dominant resource concerns
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Ponding and flooding
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Plant productivity and health
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Plant structure and composition
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Plant pest pressure
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Terrestrial habitat for wildlife and invertebrates
Community 2.1
Invasiveness and Biological Introductions
Introduction of invasive species, pathogens, and/or pests resulting in shifts in ecological site composition, functionality, and dynamics. More research is needed to determine the extent of these effects on the semi-natural state associated with this ecological site.
Community 2.2
Ponded
Site may transition to a ponded environment under certain ecological conditions or constraints such as increased annual/decadal precipitation or significant increase in flooding events.
Dominant resource concerns
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Ponding and flooding
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Plant productivity and health
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Plant structure and composition
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Plant pest pressure
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Terrestrial habitat for wildlife and invertebrates
Community 3.1
Grass/Hayland
Site transitioned to grassland for pasture or grazing or cultivated for hay production.
Dominant resource concerns
Transition T1A
State 1 to 2
climate change, hydrological alteration, significant increase in flooding events and annual precipitation, introduction of invasive species, pests, and pathogens
Monitoring and Evaluation |
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Transition T1B
State 1 to 3
hydrologic alteration (barrier, obstruction, dam, diversion), landscape alteration, mechanical soil disturbance, landscape alteration, planting, seeding
Cover Crop |
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Land Clearing |
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Precision Land Forming |
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Irrigation Land Leveling |
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Land Smoothing |
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Spoil Spreading |
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Grazing Management Plan |
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Grazing management to improve wildlife habitat |
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Harvest hay in a manner that allows wildlife to flush and escape |
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Monitoring and Evaluation |
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Restoration pathway R2A
State 2 to 1
remediation of hydrologic alteration, management of invasive species, pests, and pathogens, restoration of key native plant species, restoration of terrestrial and aquatic habitat
Restoration and Management of Rare and Declining Habitats |
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Upland Wildlife Habitat Management |
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Invasive Plant Species Control |
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Pathogen Management |
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Invasive Species Pest Management |
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Restoration and Management of Rare or Declining Habitats |
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Multi-species Native Perennials for Biomass/Wildlife Habitat |
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Habitat Development for Beneficial Insects for Pest Management |
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Biological suppression and other non-chemical techniques to manage brush, weeds and invasive species |
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Biological suppression and other non-chemical techniques to manage herbaceous weeds invasive species |
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Monitoring and Evaluation |
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Herbaceous Weed Control |
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Transition T2A
State 2 to 3
hydrologic alteration (barrier, obstruction, dam, diversion), landscape alteration, mechanical soil disturbance, landscape alteration, planting, seeding
Cover Crop |
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Land Clearing |
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Precision Land Forming |
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Irrigation Land Leveling |
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Land Smoothing |
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Spoil Spreading |
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Monitoring and Evaluation |
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Restoration pathway R3B
State 3 to 1
remediation of hydrologic alteration, seeding, planting, significant flooding events and increase in annual precipitation, compacted soil, establishment of key native plant species
Restoration and Management of Rare and Declining Habitats |
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Upland Wildlife Habitat Management |
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Restoration and Management of Natural Ecosystems |
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Native Plant Community Restoration and Management |
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Monitoring and Evaluation |
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Restoration pathway R3A
State 3 to 2
remediation of hydrologic alteration, seeding, planting, significant flooding events and increase in annual precipitation, compacted soil, establishment of key native plant species
Restoration and Management of Rare and Declining Habitats |
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Upland Wildlife Habitat Management |
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Restoration and Management of Natural Ecosystems |
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Native Plant Community Restoration and Management |
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Monitoring and Evaluation |
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