Natural Resources
Conservation Service
Ecological site F143XY220ME
Semi-Acidic Peat Wetland Complex
Last updated: 10/07/2024
Accessed: 12/03/2024
General information
Provisional. A provisional ecological site description has undergone quality control and quality assurance review. It contains a working state and transition model and enough information to identify the ecological site.
MLRA notes
Major Land Resource Area (MLRA): 143X–Northeastern Mountains
MLRA 143 is in Maine (51 percent), New York (27 percent), Vermont (13 percent), New Hampshire (7 percent), and Massachusetts (2 percent). It makes up about 34,409 square miles (89,118 square kilometers). The MLRA consists of rolling hills and mountains covered by Wisconsin till. It is in three parts separated by other MLRAs. The western part is in New York (primarily the Adirondack Mountains). The central part is mainly in the Green Mountains in Vermont and the Berkshires in Massachusetts. The eastern part is in New Hampshire and most of northern Maine. The MLRA is used mainly for forestry and recreational purposes. The western part of MLRA 143 in the Adirondack Mountains has a distinct boundary with the physiographical dissimilar Saint Lawrence-Champlain Plain. The middle part that encompasses the Green Mountains has a diffuse boundary as it blends into the northern part of the New England and Eastern New York Uplands on the foothills of the Green Mountains. The southern boundary of the easternmost part of MLRA 143 has the same diffuse boundary. The northern boundary of the MLRA is the Canadian border.
The westernmost part of this MLRA is primarily in the Adirondack province of the Appalachian Highlands. A small area in the southern end of the western part is in the Mohawk section of the Appalachian Plateaus province of the same division. The easternmost part, primarily in northern Maine, is in the New England Upland section of the New England province of the Appalachian Highlands. The southwestern half of this part is in the White Mountain section of the same province and division, and the middle part of the MLRA is in the Green Mountain section. The mountains and foothills in this MLRA are commonly rounded. They are underlain by bedrock and typically covered with thin deposits of till. The more rugged mountain areas are separated by high-gradient streams coursing through steep areas of colluvium or talus-laden valleys. Many glacially broadened valleys are filled with glacial outwash and have numerous swamps and lakes. The mountains and foothills are moderately steep to very steep, and the valleys are nearly level to sloping.
As the northernmost MLRA in the region with the coldest temperatures and shortest growing season, the Northeastern Mountains have less overall tree diversity, fewer pine and oak trees, and more abundant spruce and fir trees than neighboring MLRAs. The variability in microtopography on this site results in a patchy mosaic of plant communities. Silver maple is the most common overstory species, with diverse grasses and herbs indicating differences in soil wetness throughout the site due to slight variability in elevation above the water table. This site is subject to ice scour and flooding, but the most extensive disturbance is cultivation. These broad, flat landforms are nutrient rich with high water-holding capacity. These factors along with their adjacency to rivers made them ideal farming locations for early settlers, much of which continues today. The effects of altered flow regimes from modern dams may also be significant but require further study.
Classification relationships
This site occurs in Ecological Site Group 2 (Open Wetlands) of MLRA 143 (The Northeastern Mountains), in the Northeastern Forage and Forest Region (Land Resource Region R).
The Northeastern Forage and Forest LRR includes all of Maine, New Hampshire, Vermont, Rhode Island, and Connecticut, as well as large portions of Massachusetts, New York, New Jersey, Pennsylvania, and Ohio. Its southern boundary marks the extent of the Wisconsin ice sheet, which engulfed the entire LRR as recently as 10,000 to 15,000 years ago. Erosional and depositional processes associated with glaciation created many of the topographic patterns that distinguish MLRAs within the Northeastern region. Harder granitic and metamorphic bedrock to the north were more resistant to glacial erosion, resulting in the relatively nutrient poor mountains of MLRA 143; whereas nutrient-rich sedimentary bedrock of MLRAs 139, 140, and 146 resulted in relatively flat, fertile landscapes ideal for cultivation. Other areas were depressed below sea-level by the sheer mass of the glacier, resulting in pockets of marine sediments which distinguish MLRAs 142, 144A, 144B, and 145.
Precipitation is sufficient to support productive forestland throughout the Northeastern region. Still, a latitudinal temperature gradient from mesic to frigid soil temperatures results in a general transition from central hardwoods and pine in the southern MLRAs to northern hardwoods and spruce-fir forests farther north (no true boreal forests exist in the region). Elevations are generally low throughout the Northeastern region, with the exception of MLRA 143 which has many high mountain ecosystems with cryic temperature regimes and alpine vegetation above the tree line.
Ecological site concept
This site occurs in flat, low-lying areas characterized by very
poorly-drained, semi-acidic peat soils and bog vegetation. Soil pH
is typically between 4.5 and 6.0 throughout, allowing for more
overall species diversity than true acid bogs, but also lacking many
true acid bog indicator species. It is dominated by sphagnum moss
and heath shrubs, and supports other common bog species such
as cotton grass in lower quantities. This site may also support low
cover of black spruce and larch trees in some areas.
This ecological site is resistant to major disturbances except for
small scale hydrologic alterations that may create small patches of
drained or ponded peatland. This ecological resistance can be
attributed to the ability of these bogs to respond to large
fluctuations in water, as well as general resistance to fire, insects,
disease, construction, land management, etc.. Further study is
needed to identify alternative states for this site.
Associated sites
F143XY230ME |
Acidic Peat Wetland Complex The Semi-acidic Peat Wetland Complex may grade into the Acidic Peat Wetland Complex, usually with the latter being toward the center of the bog and grading outward to be less acidic toward the surrounding forested land. |
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Similar sites
F143XY230ME |
Acidic Peat Wetland Complex The Acidic Peat Wetland Complex has pH less than 4.5 throughout the profile, compared to pH of greater than 4.5 in at least part of the profile for the Semi-acidic Peat Wetland Complex site. The lower pH result in the most acid bog vegetation indicators, such as pitcher plant and sundew. |
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F143XY210ME |
Marsh Wetland Complex The Marsh Wetland Complex occurs in a similar landscape position, but has more nutrient and oxygen-rich soil water conditions, resulting in the decomposition of organic matter into muck, rather than the peat accumulation characteristic of the Semi-acidic Peat Wetland Complex. |
Table 1. Dominant plant species
Tree |
(1) Acer saccharinum |
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Shrub |
Not specified |
Herbaceous |
Not specified |
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