Natural Resources
Conservation Service

Ecological site F101XY009NY

Moist Lake Plain

Last updated: 10/03/2024
Accessed: 12/22/2024

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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): 101X–Ontario-Erie Plain and Finger Lakes Region

Most of the MLRA is a nearly level to rolling plain. Low remnant beach ridges are commonly interspersed with a relatively level lake plain in the northern part of the area. Drumlins (long, narrow, steep-sided, cigar shaped hills) are prominent in an east-west belt in the center of the area. The Finger Lakes Region consists of a gently sloping to rolling till plain. Elevation t increases gradually from the shores of Lake Ontario and Lake Oneida to the Allegheny Plateau, the southern border of the area. The bedrock underlying this area consists of alternating beds of limestone, dolomite, sandstone, and shale of Ordovician to Devonian age. Most of the surface of the area is covered with glacial till or lake sediments. The texture of the lake sediments is silt, loam, or sand. Ancient beaches, formed at different lake levels, form ridges along the shoreline of Lake Erie and Lake Ontario. Stratified drift (eskers and kames) and glacial outwash deposits are in many of the valleys. A large drumlin field occurs in the Finger Lakes Region.

Classification relationships

USDA-NRCS (USDA, 2006):
Land Resource Region (LRR): L — Lake States Fruit, Truck Crop, and Dairy Region
Major Land Resource Area (MLRA): 101— Ontario-Erie Plain and Finger Lakes Region
USDA-FS (Cleland et al., 2007)
Province: 211 — Northeastern Mixed Forest Province (in part)
Section: 211J — Mohawk Valley (in part)
Subsection: 211Jd — Mohawk Valley
Province: 222 — Midwest Broadleaf Forest Province (in part)
Section: 222I — Erie and Ontario Lake Plain
Subsection: 222Ia — Lake Erie Plain
222Ib — Erie-Ontario Lake Plain
222Ic — Eastern Ontario Till Plain
222Id — Cattaraugus Finger Lakes Moraine and Hills
222Ie — Eastern Ontario Lake Plain

Ecological site concept

Landform/Landscape Position:
The site occurs on lake plains and lacustrine terraces. Slopes range from 0 to 25 percent.

Soils:
The site consists of moderately deep to very deep, moderately well drained or somewhat poorly drained soils formed in glaciolacustrine deposits. Soil textures are mostly fine or fine silty. Representative soils are Barcelona, Cayuga, Churchville, Collamer, Elmwood, Hudson, Rhinebeck, Schoharie, Tonawanda, Niagara, Odessa, Wallington, and Williamson.

Vegetation
The reference community coincides with NY Natural Heritage Community: Maple-basswood rich mesic forest.

Associated sites

F101XY010NY	Wet Lake Plain Depression Wet Lake Plain Depression sites are lower in the landscape profile.
F101XY012NY	Till Upland

F101XY010NY

Wet Lake Plain Depression

Wet Lake Plain Depression sites are lower in the landscape profile.

F101XY012NY

Till Upland

Similar sites

F101XY006NY	Moist Outwash Moist Outwash is typically less enriched.
F101XY013NY	Moist Till Moist Till may be considered less enriched.

F101XY006NY

Moist Outwash

Moist Outwash is typically less enriched.

F101XY013NY

Moist Till

Moist Till may be considered less enriched.

Table 1. Dominant plant species

Tree	(1) Acer saccharum (2) Tilia americana
Shrub	(1) Acer spicatum (2) Hamamelis virginiana
Herbaceous	(1) Polystichum acrostichoides (2) Trillium cernuum

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Physiographic features

The site occurs on lake plains and lacustrine terraces. Slopes range from 0 to 25 percent.

Table 2. Representative physiographic features

Landforms	(1) Lake plain > Lake plain (2) Till plain > Lake terrace (3) Depression (4) Terrace (5) Outwash terrace
Runoff class	Very low to very high
Flooding frequency	None
Ponding frequency	None
Elevation	24 – 750 m
Slope	0 – 25%
Water table depth	18 – 76 cm
Aspect	Aspect is not a significant factor

Climatic features

The Koppen-Geiger climate classification of the area in which this MLRA occurs is
Dfb, Warm-summer humid continental. Rainfall occurs as high-intensity, convective thunderstorms in the summer. However, snow comprises most of the precipitation in this area. The frost-free-free period in this area averages 165 days and ranges from 130 to 200 days, with the coldest temperatures and the shortest frost-free periods occurring in the high-elevation areas in the eastern part of the MLRA.

Table 3. Representative climatic features

Frost-free period (characteristic range)	136-140 days
Freeze-free period (characteristic range)	173-186 days
Precipitation total (characteristic range)	940-1,067 mm
Frost-free period (actual range)	135-140 days
Freeze-free period (actual range)	167-187 days
Precipitation total (actual range)	889-1,067 mm
Frost-free period (average)	138 days
Freeze-free period (average)	179 days
Precipitation total (average)	991 mm

Characteristic range

Actual range

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Figure 1. Monthly precipitation range

Characteristic range

Actual range

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Figure 2. Monthly minimum temperature range

Characteristic range

Actual range

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Figure 3. Monthly maximum temperature range

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Figure 4. Monthly average minimum and maximum temperature

Figure 5. Annual precipitation pattern

Figure 6. Annual average temperature pattern

Climate stations used

(1) SUNY ESF SYRACUSE [USC00308386], Syracuse, NY
(2) DELANSON 2NE [USC00302031], Delanson, NY
(3) ROCHESTER GTR INTL AP [USW00014768], Rochester, NY
(4) DUNKIRK CHAUTAUQUA AP [USW00014747], Dunkirk, NY
(5) LOCKPORT 3 S [USC00304844], Lockport, NY

Soil features

The site consists of moderately deep to very deep, moderately well drained or somewhat poorly drained soils formed in glaciolacustrine deposits. Soil textures are mostly fine or fine silty. Representative soils are Barcelona, Cayuga, Churchville, Collamer, Elmwood, Hudson, Rhinebeck, Schoharie, Tonawanda, Niagara, Odessa, Wallington, Elmridge, Scio, and Williamson.

Table 4. Representative soil features

Parent material	(1) Glaciolacustrine deposits – limestone, sandstone, and shale (2) Till (3) Alluvium (4) Eolian deposits
Surface texture	(1) Silt loam (2) Silty clay loam (3) Fine sandy loam (4) Gravelly loam (5) Very fine sandy loam
Family particle size	(1) Coarse-loamy over clayey (2) Coarse-silty (3) Fine (4) Fine-silty (5) Loamy
Drainage class	Somewhat poorly drained to well drained
Permeability class	Very slow to moderately slow
Depth to restrictive layer	38 – 183 cm
Surface fragment cover <=3"	0%
Surface fragment cover >3"	0%
Available water capacity (Depth not specified)	7.62 – 20.32 cm
Soil reaction (1:1 water) (Depth not specified)	3.5 – 8.4
Subsurface fragment volume <=3" (Depth not specified)	0 – 34%
Subsurface fragment volume >3" (Depth not specified)	0 – 27%

Ecological dynamics

The reference coincides with Maple-Basswood Rich Mesic Forest (NY Natural Heritage Program) and International Vegetation Classification Sugar Maple – American Basswood / Blue Cohosh Forest
Acer saccharum – Tilia americana / Caulophyllum thalictroides Forest (CEGL006637)

Common trees are sugar maple, northern red oak, basswood, yellow birch, white ash, and hop hornbeam. Shrubs include striped maple, witch-hazel, and dogwood. Dynamics includes conversion of site into agricultural production and invasive species establishment. Disturbances include wind, ice, insects, and land clearing or timber harvest.

State and transition model

More interactive model formats are also available. View Interactive Models
Click on state and transition labels to scroll to the respective text

State 1
Reference - Minimally Managed

Reference is Maple-basswood rich mesic forest. Natural disturbances such and wind and ice storms, tree fall, insect damage will create openings for an early successional plant community or young forest. This forest may have at one time been cleared or plowed during colonial times.

Characteristics and indicators. Soil may have evidence of an historic plow layer (Ap horizon).

Resilience management. Ensure that regenerating trees and shrubs are not heavily browsed by deer that they cannot replace overstory trees. Deer have been shown to have negative effects on forest understories (New York Natural Heritage Program, 2020). Avoid cutting old-growth forests.

Community 1.1
Mature Forest

Mature, late successional closed canopy forest. The reference community coincides with NY natural heritage community: Rich mesophytic forest.

Community 1.2
Young Forest

Open canopy, early successional, young forest.

Pathway P1.1
Community 1.1 to 1.2

Natural disturbances - wind/ice storm, tree fall, and insect damage.

Conservation practices

Early Successional Habitat Development/Management

Pathway P1.2
Community 1.2 to 1.1

Time (succession).

State 2
Managed Timber

The state is characterized by active logging. Composition of forest stands will vary based on management objectives.

Community 2.1
Managed Timber

State 3
Minimally Managed Forest with Invasive Species.

Invasive species such as Japanese barberry, bush honeysuckle, multiflora rose, garlic mustard, and stiltgrass are common in the understory.

Community 3.1
Oak-pine forest with invasive species

State 4
Pasture/Grassland

Forest has been cleared and grasses and forbs have been introduced for livestock grazing, hay production, and/or wildlife.

Community 4.1
Introduced grasses and forbs

Community 4.2
Woody plant encroachment

Pathway P4.1
Community 4.1 to 4.2

Abandonment (lack of mowing or fire suppression)

Pathway P4.2
Community 4.2 to 4.1

Mowing, prescribed fire, and/or brush management.

Conservation practices

Brush Management

Transition T1A
State 1 to 2

Timber harvest; logging.

Transition T1B
State 1 to 3

Introduction of invasive species usually after disturbance.

Transition T1C
State 1 to 4

Land use conversion.

Restoration pathway R2A
State 2 to 1

Time (succession). Forest stand improvement, restoration.

Transition T2A
State 2 to 3

Introduction of invasive species. Lack of timber management.

Transition T2B
State 2 to 4

Land use conversion

Restoration pathway R3A
State 3 to 1

Brush management, invasive species management.

Transition T3A
State 3 to 2

Timber management/harvest, logging.

Transition T3B
State 3 to 4

Land use conversion.

Restoration pathway R4A
State 4 to 1

Abandonment, Time (succession), forest restoration.

Restoration pathway R4A
State 4 to 3

Abandonment, time (sucession) and introduction of invasive species.

Additional community tables

Supporting information

Inventory data references

Site Development and Testing Plan:
Future work to validate the vegetation information in this provisional ecological site description is needed. This will include field activities to collect low and medium intensity sampling and analysis of that data. Field reviews should be done by soil scientists and vegetation specialists. A final field review, peer review, quality control, and quality assurance reviews of the ESD will be needed to produce the final approved level document. Reviews of the project plan are to be conducted by the Ecological Site Technical Team.

Other references

Cleland, D.T., J.A. Freeouf, J.E. Keys, G.J. Nowacki, C. Carpenter, and W.H. McNab. 2007. Ecological Subregions, Sections, and Subsections of the Coterminous United States. USDA Forest Service, General Technical Report WO-76. Washington, DC.

Cowardin L. M., Carter V., Golet F. C., and LaRoe E.T. 1979. Classification of Wetlands and Deepwater Habitats of the United States. U.S. Fish and Wildlife Service. U.S. Government Printing Office, Washington, D.C., 20402.

Edinger, G.J., Evans, D.J., Gebauer, S., Howard, T.G., Hunt, D.M., and A.M. Olivero, A.M. (eds.). 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.

NatureServe 2018. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://explorer.natureserve.org. (Accessed: January 2019).

USDA-NRCS [United States Department of Agriculture, Natural Resources Conservation Service] 2006. Land Resource Regions and Major land Resource Areas of the United States, the Caribbean, and the Pacific Basin. U.S. Department of Agriculture Handbook 296.

USDA-NRCS [United States Department of Agriculture, Natural Resources Conservation Service] 2016. National Soils Information System (NASIS) [Software] Version 7.x. USDA, Kansas City, MO.

USNVC [United States National Vegetation Classification]. 2017. United States National Vegetation Classification Database, V2.01. Federal Geographic Data Committee, Vegetation Subcommittee, Washington DC. http://usnvc.org/explore-classification/ (Accessed: 2018).

Contributors

Joshua Hibit

Approval

Greg Schmidt, 10/03/2024

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	05/21/2020
Approved by	Greg Schmidt
Approval date
Composition (Indicators 10 and 12) based on	Annual Production

Indicators

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:

Download reference sheet

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Natural ResourcesConservation Service

Ecological site F101XY009NY

Moist Lake Plain

Last updated: 10/03/2024 Accessed: 12/22/2024

General information

MLRA notes

Classification relationships

Ecological site concept

Associated sites

Similar sites

Table 1. Dominant plant species

Ecosystem states

State 1 submodel, plant communities

State 2 submodel, plant communities

State 3 submodel, plant communities

State 4 submodel, plant communities

Natural Resources
Conservation Service

Last updated: 10/03/2024
Accessed: 12/22/2024