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Natural Resources
Conservation Service
Ecological site F144BY601ME
Dry Sand
Last updated: 6/29/2020
Accessed: 08/16/2024
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): 144B–New England and Eastern New York Upland, Northern Part
Major Land Resource Area (MLRA): 144B–New England and Eastern New York Upland, Northern Part
This major land resource area (MLRA) is characterized by plateaus, plains, and mountains. The climate is generally cool and humid with an average annual precipitation of 34 to 62 inches (865 to 1,575 millimeters). The average annual air temperature is typically 40 to 48 degrees F (4 to 9 degrees C). The freeze-free period generally is 130 to 200 days, but it ranges from 110 days in the higher mountains to 240 days in some areas along the Atlantic coast. The soils in this region are dominantly Entisols, Spodosols, and Inceptisols. They commonly have a fragipan. The dominant suborders are Ochrepts, Orthods, Aquepts, Fluvents, and Saprists. The soils in the region dominantly have a frigid soil temperature regime with some cryic areas at higher elevation, a udic soil moisture regime, and mixed mineralogy. Most of the land is forested, and 98 percent is privately owned. Significant amounts of forest products are produced including lumber, pulpwood, Christmas trees, and maple syrup. Principal agricultural crops include forage and grains for dairy cattle, potatoes, apples, and blueberries. Wildlife habitat and recreation are important land uses. Stoniness, steep slopes, and poor drainage limit the use of many of the soils.
Classification relationships
NRCS:
Land Resource Region: R—Northeastern Forage and Forest Region
MLRA: 144B—New England and Eastern New York Upland, Northern Part
Table 1. Dominant plant species
Tree |
(1) Pinus strobus |
---|---|
Shrub |
Not specified |
Herbaceous |
Not specified |
Physiographic features
This site usually occurs on landforms comprised of sandy glacial outwash deposits such as eskers, kame terraces and outwash plains, and can also occur on sandy till deposits such as moraines and till plains. It can be found from sea level to 3810 feet on slopes ranging from 0 to 45 percent, sometimes up to 60 percent.
Table 2. Representative physiographic features
Landforms |
(1)
Outwash plain
(2) Esker (3) Terrace |
---|---|
Flooding frequency | None |
Ponding frequency | None |
Elevation | 3,810 ft |
Slope | 60% |
Ponding depth | 6 in |
Water table depth | 72 in |
Aspect | W, NW, N, NE, E, SE, S, SW |
Climatic features
The climate is humid and temperate. It is characterized by warm summers and cold winters. The average first frost around October 1st and the last freeze of the season occurs around April 23rd. Temperature extremes in the summer can reach as high as 100 degrees F and as low as -33 degrees F in the winter. The average relative humidity is 71 percent. The sun shines on average 57 percent of the time. Bad storm events can come in from the northeast, thus the term “nor’easter”. Winter blizzards can result in several feet of snow, while summer hurricane events can produce 2-3 inches of rain per hour. Annual rainfall occurs quite evenly over the entire year with August being the driest month during the growing season from April through September. Rainfall during this period generally falls during thunderstorms, and fairly large amounts of rain may fall in a short time. Eighty-eight percent of the snowfall occurs from December through March and average total snowfall is 64 inches per year. This makes for a “mud season” from March through April where runoff is high and ponding may occur because surface water runoff is very slow. The original data used in developing the table below was obtained from the USDA-NRCS National Water & Climate Center climate information database. All the climate station monthly averages for maximum and minimum temperature and precipitation were then added together and averaged to make this table. The precipitation and temperature data come from the years 1981 through 2010.
Table 3. Representative climatic features
Frost-free period (characteristic range) | 117-140 days |
---|---|
Freeze-free period (characteristic range) | 144-170 days |
Precipitation total (characteristic range) | 42-48 in |
Frost-free period (actual range) | 98-146 days |
Freeze-free period (actual range) | 133-180 days |
Precipitation total (actual range) | 40-54 in |
Frost-free period (average) | 126 days |
Freeze-free period (average) | 159 days |
Precipitation total (average) | 46 in |
Figure 1. Monthly precipitation range
Figure 2. Monthly minimum temperature range
Figure 3. Monthly maximum temperature range
Figure 4. Monthly average minimum and maximum temperature
Figure 5. Annual precipitation pattern
Figure 6. Annual average temperature pattern
Climate stations used
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(1) BELFAST [USC00170480], Belfast, ME
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(2) ACADIA NP [USC00170100], Bar Harbor, ME
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(3) CORINNA [USC00171628], Corinna, ME
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(4) DOVER-FOXCROFT WWTP [USC00171975], Dover Foxcroft, ME
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(5) FARMINGTON [USC00172765], Farmington, ME
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(6) GARDINER [USC00173046], Gardiner, ME
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(7) JONESBORO [USC00174183], Addison, ME
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(8) LEWISTON [USC00174566], Auburn, ME
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(9) MADISON [USC00174927], Anson, ME
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(10) NEWCASTLE [USC00175675], Newcastle, ME
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(11) ORONO [USC00176430], Old Town, ME
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(12) WATERVILLE TRTMT PLT [USC00179151], Waterville, ME
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(13) WEST ROCKPORT 1 NNW [USC00179593], Rockport, ME
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(14) AUGUSTA STATE AP [USW00014605], Augusta, ME
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(15) BANGOR INTL AP [USW00014606], Bangor, ME
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(16) PORTLAND INTL JETPORT [USW00014764], Portland, ME
Influencing water features
This site is not influenced by streams or wetlands.
Soil features
The soils of this site are sandy throughout, sometimes with a thin sandy loam surface horizon. They formed in glaciofluvial deposits or meltout till deposited by receding glaciers. Rock fragments may or may not be present on the soil surface and throughout the profile. These soils are well- to excessively-drained.
The representative soils are Colton, Adams, Monadnock, Hermon, Udipsamments, Masardis, Hinckley, Windsor, Merrimac, Champlain, Boscawen, Gloucester, Duxbury, Groton, Stetson, Masardis variant, Teago, Pomfret, Windsor variant, and Caesar.
Table 4. Representative soil features
Parent material |
(1)
Glaciofluvial deposits
–
igneous and metamorphic rock
(2) Supraglacial meltout till |
---|---|
Surface texture |
(1) Loamy sand (2) Sandy loam (3) Fine sandy loam |
Drainage class | Excessively drained to well drained |
Soil depth | 60 in |
Surface fragment cover <=3" | Not specified |
Surface fragment cover >3" | 2% |
Available water capacity (Depth not specified) |
1 – 7 in |
Soil reaction (1:1 water) (Depth not specified) |
3.5 – 6.5 |
Ecological dynamics
This site is typically dominated by red pine, white pine, and/or red spruce. Hemlock and other softwood species may also be abundant, and scattered hardwoods may be present. The understory is generally sparse.
On gentler slopes, this site has been cleared and cultivated for pasture/hayland or crop production. Blueberries are particularly suited to these sandy soils.
Gravel and sand mining are common on this site, and often accompanied by heavy logging to remove timber prior to soil excavation. Following cutting, early successional species such as fir, white birch, pin cherry, and aspen may enter the community, but they die out as the forest reaches maturity within about 80 years.
Further study is required to understand plant community dynamics on this site.
This site includes the following state natural heritage program types:
• Red and White Pine Forest (Sperduto and Nichols 2004)
• Red and White Pine Forests (Gawler and Cutko 2010)
• White Pine Forests (Gawler and Cutko 2010)
State and transition model
![Model diagram](https://edit.jornada.nmsu.edu/uploads/med/da/zw/1584384485_333917.jpg)
More interactive model formats are also available.
View Interactive Models
More interactive model formats are also available.
View Interactive Models
Click on state and transition labels to scroll to the respective text
State 1 submodel, plant communities
Communities 1, 5 and 2 (additional pathways)
State 2 submodel, plant communities
State 3 submodel, plant communities
State 4 submodel, plant communities
State 1
Reference/ Current Potential
Community 1.1
Old Pine - Spruce Forest Phase: 120+Yrs
120+ year old forest, typically dominated by red pine, white pine and/or red spruce.
Dominant plant species
-
eastern white pine (Pinus strobus), tree
-
red spruce (Picea rubens), tree
Community 1.2
Pine Seedling/ Herbaceous Phase
White pine seedlings often dominate, with ferns, wild raspberry, and other colonizers.
Dominant plant species
-
eastern white pine (Pinus strobus), tree
Community 1.3
Successional Forest Phase
Diverse young spruce, pine, birch, aspen, etc.
Community 1.4
Intermediate Forest Phase: 50 - 80 yrs
50-80 year old softwoods. Early successional species dying out.
Community 1.5
Mature Forest Phase: 80 - 120 yrs
80-120 year old hardwoods and softwoods.
Pathway P1.1-1.2
Community 1.1 to 1.2
clearcutting, blowdown, fire
Pathway P1.2-1.3
Community 1.2 to 1.3
vegetation development (succession)
Pathway P1.3-1.2
Community 1.3 to 1.2
selective cutting, forest management
Conservation practices
Forest Stand Improvement | |
---|---|
Forest Land Management | |
Forest Management Plan - Written | |
Forest Management Plan - Applied |
Pathway P1.3-1.4
Community 1.3 to 1.4
vegetation development (succession)
Pathway P1.4-1.2
Community 1.4 to 1.2
selective cutting, forest management
Conservation practices
Forest Stand Improvement | |
---|---|
Forest Land Management | |
Forest Management Plan - Written | |
Forest Management Plan - Applied |
Pathway P1.4-1.3
Community 1.4 to 1.3
selective cutting, forest management
Conservation practices
Forest Stand Improvement | |
---|---|
Forest Land Management | |
Forest Management Plan - Written | |
Forest Management Plan - Applied |
Pathway P1.4-1.5
Community 1.4 to 1.5
vegetation development (succession)
Pathway P1.5-1.1
Community 1.5 to 1.1
cutting, logging, fire
Conservation practices
Upland Wildlife Habitat Management | |
---|---|
Forest Trails and Landings | |
Forest Stand Improvement | |
Record Keeping | |
Forest Land Management | |
Forest Management Plan - Written | |
Forest Management Plan - Applied | |
Forest stand improvement for habitat and soil quality |
Pathway P1.5-1.2
Community 1.5 to 1.2
selective cutting, forest management
Pathway P1.5-1.4
Community 1.5 to 1.4
selective cutting thinning, forest management
Conservation practices
Forest Stand Improvement | |
---|---|
Forest Land Management | |
Forest Management Plan - Written | |
Forest Management Plan - Applied |
State 2
Pasture
Community 2.1
Pasture/Hay Phase
Cleared and cultivated fields of mostly perennial herbaceous species.
State 3
Cropland
Cleared and cultivated fields, heavily managed with significant inputs and/or regular soil disturbance. (e.g. blueberry production).
Community 3.1
Annual or Perennial Crop Phase
: Cleared and cultivated fields, heavily managed with significant inputs and/or regular soil disturbance. (e.g. blueberry production).
State 4
Gravel Pits
Community 4.1
Active Gravel Pit Phase
Weedy barrens. Some wild raspberry, ferns, and other herbs colonize the open land
Community 4.2
Successional Forest Phase
Diverse young spruce, pine, and early successional species (white birch, aspen, blasam fir, etc).
Pathway P4.1-4.2
Community 4.1 to 4.2
abandonment, vegetation development (succession)
Conservation practices
Tree/Shrub Site Preparation | |
---|---|
Tree/Shrub Establishment |
Pathway P4.2-4.1
Community 4.2 to 4.1
clearing and cutting
Conservation practices
Clearing and Snagging | |
---|---|
Land Clearing |
Transition T1-2
State 1 to 2
Cutting and clearing, meadow/pasture establishment
Conservation practices
Brush Management | |
---|---|
Clearing and Snagging | |
Land Clearing | |
Upland Wildlife Habitat Management | |
Early Successional Habitat Development/Management | |
Record Keeping | |
Native Plant Community Restoration and Management | |
Invasive Species Pest Management |
Transition T1-3
State 1 to 3
cutting and clearing, crop establishment
Conservation practices
Clearing and Snagging | |
---|---|
Land Clearing | |
Land Smoothing | |
Record Keeping |
Transition T1-4
State 1 to 4
cutting and clearing, sand and gravel mining operations (excavation)
Conservation practices
Clearing and Snagging | |
---|---|
Land Clearing | |
Monitoring and Evaluation |
Restoration pathway R2-1
State 2 to 1
abandonment, vegetation development (succession), plantings
Conservation practices
Brush Management | |
---|---|
Tree/Shrub Site Preparation | |
Tree/Shrub Establishment | |
Upland Wildlife Habitat Management | |
Record Keeping | |
Invasive Plant Species Control |
Transition T2-4
State 2 to 4
sand and gravel excavation
Conservation practices
Land Clearing | |
---|---|
Monitoring and Evaluation |
Restoration pathway R3-1
State 3 to 1
abandonment, vegetation development (succession), plantings
Conservation practices
Tree/Shrub Site Preparation | |
---|---|
Tree/Shrub Establishment | |
Upland Wildlife Habitat Management | |
Record Keeping | |
Invasive Plant Species Control |
Transition T3-4
State 3 to 4
sand and gravel excavation
Conservation practices
Land Clearing | |
---|---|
Monitoring and Evaluation |
Restoration pathway R4-1
State 4 to 1
forest re-establishment
Conservation practices
Tree/Shrub Site Preparation | |
---|---|
Land Reclamation, Abandoned Mined Land | |
Land Reclamation, Currently Mined Land | |
Spoil Spreading | |
Tree/Shrub Establishment | |
Upland Wildlife Habitat Management | |
Land Grading | |
Record Keeping | |
Restoration and Management of Natural Ecosystems | |
Native Plant Community Restoration and Management | |
Invasive Plant Species Control |
Additional community tables
Interpretations
Supporting information
Inventory data references
Site Development and Testing Plan
Future work is needed, as described in a project plan, to validate the information presented in this provisional ecological site description. Future work includes field sampling, data collection and analysis by qualified vegetation ecologists and soil scientists. As warranted, annual reviews of the project plan can be conducted by the Ecological Site Technical Team. A final field review, peer review, quality control, and quality assurance reviews of the ESD are necessary to approve a final document.
Other references
Gawler, S. and A. Cutko. 2010. Natural Landscapes of Maine. A Guide to Natural Communities and Ecosystems. Maine Natural Areas Program, Maine Department of Conservation, Augusta, ME.
Johanson, J. K., Butler, N. R. and C. Bickford. 2016. Classifying Northern New England Landscapes for Improved Conservation. Rangelands 38:6.
Sperduto, D.D. and W.F. Nichols. 2004. Natural Communities of New Hampshire. New Hampshire Natural Heritage Bureau and The Nature Conservancy.
USDA NRCS 2006. Land resource regions and major land resource areas of the United States, the Caribbean, and the Pacific Basin. USDA Handbook 296.
Contributors
Jamin Johanson
Nick Butler
Carl Bickford
Approval
Nels Barrett, 6/29/2020
Acknowledgments
Nels Barrett, Ph.D
Rangeland health reference sheet
Interpreting Indicators of Rangeland Health is a qualitative assessment protocol used to determine ecosystem condition based on benchmark characteristics described in the Reference Sheet. A suite of 17 (or more) indicators are typically considered in an assessment. The ecological site(s) representative of an assessment location must be known prior to applying the protocol and must be verified based on soils and climate. Current plant community cannot be used to identify the ecological site.
Author(s)/participant(s) | |
---|---|
Contact for lead author | |
Date | 09/09/2022 |
Approved by | Nels Barrett |
Approval date | |
Composition (Indicators 10 and 12) based on | Annual Production |
Indicators
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Number and extent of rills:
-
Presence of water flow patterns:
-
Number and height of erosional pedestals or terracettes:
-
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
-
Number of gullies and erosion associated with gullies:
-
Extent of wind scoured, blowouts and/or depositional areas:
-
Amount of litter movement (describe size and distance expected to travel):
-
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
-
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
-
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
-
Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on this site):
-
Functional/Structural Groups (list in order of descending dominance by above-ground annual-production or live foliar cover using symbols: >>, >, = to indicate much greater than, greater than, and equal to):
Dominant:
Sub-dominant:
Other:
Additional:
-
Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
-
Average percent litter cover (%) and depth ( in):
-
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
-
Potential invasive (including noxious) species (native and non-native). List species which BOTH characterize degraded states and have the potential to become a dominant or co-dominant species on the ecological site if their future establishment and growth is not actively controlled by management interventions. Species that become dominant for only one to several years (e.g., short-term response to drought or wildfire) are not invasive plants. Note that unlike other indicators, we are describing what is NOT expected in the reference state for the ecological site:
-
Perennial plant reproductive capability:
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