Natural Resources
Conservation Service

Ecological site F101XY001NY

High Floodplain

Last updated: 10/02/2024
Accessed: 11/21/2024

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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 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 floodplains adjacent to low gradient streams and rivers. Slopes range from 0 to 3 percent.

Soils:
The site consists of very deep, well drained soils that have formed in recent alluvium along streams. Representative soils are Geneseo, Hamlin, and Tioga.

Vegetation
The reference community coincides with NY natural heritage community: Floodplain forest and NatureServe’s Sugar Maple - Ash species - American Basswood / Ostrich Fern - White Snakeroot Floodplain Forest (CEGL006114).

Associated sites

F101XY003NY	Low Floodplain Depression Low Floodplain Depression is an associated feature in the broader floodplain landscape.

F101XY003NY

Low Floodplain Depression

Low Floodplain Depression is an associated feature in the broader floodplain landscape.

Similar sites

F101XY002NY	Low Floodplain Low Floodplain sites in transition to high floodplain may be similar.

F101XY002NY

Low Floodplain

Low Floodplain sites in transition to high floodplain may be similar.

Table 1. Dominant plant species

Tree	(1) Acer saccharum (2) Tilia americana
Shrub	Not specified
Herbaceous	(1) Matteuccia struthiopteris (2) Ageratina altissima

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Physiographic features

The site occurs on floodplains adjacent to low gradient streams and rivers. Slopes range from 0 to 3 percent.

Table 2. Representative physiographic features

Landforms	(1) Valley > Flood plain
Runoff class	Low
Flooding frequency	Rare to frequent
Elevation	55 – 914 m
Slope	0 – 3%
Water table depth	84 – 183 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 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

Bar

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Figure 1. Monthly precipitation range

Characteristic range

Actual range

Bar

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Figure 2. Monthly minimum temperature range

Characteristic range

Actual range

Bar

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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 very deep, well drained soils that have formed in recent alluvium along streams. Representative soils are Geneseo, Hamlin, and Tioga.

Table 4. Representative soil features

Parent material	(1) Alluvium – shale and siltstone (2) Alluvium – limestone
Surface texture	(1) Silt loam (2) Loam (3) Silty clay loam (4) Fine sandy loam
Family particle size	(1) Coarse-silty (2) Coarse-loamy (3) Fine-silty (4) Loamy
Drainage class	Well drained
Permeability class	Very slow to moderately slow
Depth to restrictive layer	183 cm
Surface fragment cover <=3"	0%
Surface fragment cover >3"	0%
Available water capacity (Depth not specified)	10.16 – 20.32 cm
Soil reaction (1:1 water) (Depth not specified)	4.5 – 8.4
Subsurface fragment volume <=3" (Depth not specified)	0 – 31%
Subsurface fragment volume >3" (Depth not specified)	0 – 6%

Ecological dynamics

Sugar Maple - Ash species - American Basswood / Ostrich Fern - White Snakeroot Floodplain Forest
Acer saccharum - Fraxinus spp. - Tilia americana / Matteuccia struthiopteris - Ageratina altissima Floodplain Forest (NatureServe CEGL006114).

These rich floodplain forests are found on slightly elevated alluvial terraces and active floodplains. Many of these forests have been converted to agricultural use. Non-native, invasive species can establish in disturbed areas.

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 - Mixed Hardwood Forest

Floodplain forest and NatureServe’s Sugar Maple - Ash species - American Basswood / Ostrich : Fern - White Snakeroot Floodplain Forest (CEGL006114).

Characteristics and indicators. Site was not cleared or cultivated historically.

Community 1.1
Old Growth Mixed Hardwood Forest

Mature closed canopy forest. Floodplain forest and NatureServe’s Sugar Maple - Ash species - American Basswood / Ostrich : Fern - White Snakeroot Floodplain Forest (CEGL006114).

Community 1.2
Young Forest

Early successional forest.

Pathway P1.1A
Community 1.1 to 1.2

Wind, flood, ice storm, insect damage.

Pathway P1.2A
Community 1.2 to 1.1

Time; succession

State 2
Managed Timber Forest

Removal of trees of commercial value. Invasive species may be present.

Community 2.1
Timber Managed Forest

Forest managed for timber, primarily oak species. Depending on type of management birch, beech, and maple may dominate following commercial timber harvest.

State 3
Invaded

Invasive species abundant. Minimally managed forest.

Community 3.1
Forest with invasive species

Non-native and invasive species present (Japanese barberry, multiflora rose, bush honeysuckle, stiltgrass.

State 4
Pastureland

Site converted to pasture for livestock grazing or hay production.

Resilience management. Must be managed (grazed, mowed, etc.) to maintain pastureland.

Community 4.1
Introduced grasses and forbs for grazing, hay production, or wildlife

Community 4.2
Woody plant encroachment

Pathway P4.1A
Community 4.1 to 4.2

Lack of management (mowing, grazing, prescribed fire)

Pathway P4.2B
Community 4.2 to 4.1

Mowing, brush management, prescribed fire.

Conservation practices

Brush Management
Prescribed Burning

State 5
Restored and/or Minimally Managed Forest

Restored forest or second-growth forest.

Characteristics and indicators. Site was cleared and/or cultivated historically.

Transition T1A
State 1 to 2

Timber harvest.

Transition T1B
State 1 to 3

Establishment of invasive species.

Transition T1C
State 1 to 4

Land use conversion.

Conservation practices

Land Clearing

Restoration pathway R2A
State 2 to 1

Conservation practices

Forest Stand Improvement
Forest Land Management
Prescribed Forestry

Transition T2A
State 2 to 4

Land use conversion

Conservation practices

Land Clearing

Restoration pathway R2B
State 2 to 5

Restoration pathway R3A
State 3 to 1

Invasive species management/removal.

Conservation practices

Invasive Plant Species Control

Transition T3A
State 3 to 4

Land use conversion

Restoration pathway R4A
State 4 to 5

Forestland restoration

Transition T5A
State 5 to 4

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.

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).

New York Natural Heritage Program. 2020. Online Conservation Guide for Floodplain forest. Available from: https://guides.nynhp.org/floodplain-forest/. (Accessed: 19 March 2020).

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, 10/02/2024

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:

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Natural ResourcesConservation Service

Ecological site F101XY001NY

High Floodplain

Last updated: 10/02/2024 Accessed: 11/21/2024

General information

MLRA notes

Classification relationships

Ecological site concept

Associated sites

Similar sites

Table 1. Dominant plant species

Ecosystem states

States 2 and 5 (additional transitions)

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: 10/02/2024
Accessed: 11/21/2024