Natural Resources
Conservation Service
Ecological site F142XA001NY
Low Floodplain
Frigid
Last updated: 10/03/2024
Accessed: 09/22/2026
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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): 142X–St. Lawrence-Champlain Plain
This MLRA is a glaciated area of low relief dominated by broad expanses of nearly level, sandy deltas and shallow lacustrine basins or plains punctuated by low hills of glacial till. Rivers and streams have cut relatively deep but narrow valleys across the plain. Elevation ranges from 80 to 1,000 feet, increasing gradually from the St. Lawrence River southward and from Lake Champlain to the east and west. Local relief generally is less than 30 feet, but glacial till ridges, till plains, and some outwash terraces rise 15 to 80 feet above the adjacent plains.
This area has been glaciated, and a thin mantle of till covers most of the bedrock. Extensive areas of sandy glacial outwash and eolian deposits also occur. Some glacial lake sediments have been deposited above glacial moraines. These deposits are thickest in the valleys and thinnest on the ridges and highlands. During the later stages of the Wisconsin glacial period, seawater entered the Champlain Valley and deposited marine sediments that were later covered by freshwater sediments. The marine deposits are unique to the area.
This area supports hardwoods. The beech-birch-sugar maple forest type is the dominant climax forest type on uplands. Associated with this type are basswood, American elm, maple species, white ash, black cherry, and white pine. The aspen-birch type, earlier in succession, is economically important. Such species as eastern hemlock, red maple, American elm, and spruce are on wet soils.
Some of the major wildlife species in this area are white-tailed deer, red fox, raccoon, beaver, woodchuck, muskrat, cottontail, ruffed grouse, and woodcock.LRU notes
Land Resource Unit (LRU): Frigid Soil Temperature Regime
The upper St. Lawrence and Champlain Valleys are characterized with soils in the frigid soil temperature regime (mean annual soil temperature greater than 32°F but less than 46°F and with a difference between mean summer and mean winter soil temperatures greater than 41°F at 20 inches below the surface or at a densic, lithic, or paralithic contact, whichever is shallower).
The Frigid Soil Temperature Regime (STR) will have shorter growing season than the lower St. Lawrence and Champlain Valleys which are characterized with soils in the mesic STR. Species more tolerant of colder year round temperatures would also be evident in the Frigid LRU.Classification relationships
NRCS:
Land Resource Region: R - Northeastern Forage and Forest Region
MLRA: 142 - St. Lawrence-Champlain Plain
LRU: A/02 - Frigid Mean Annual Soil Temperature
USFS:
Domain: 200 - Humid Temperate
Division: 210 - Warm Continental
Province: 211 - Northeastern Mixed Forest
Section: 211E - St. Lawrence and Champlain Valley
Subsections: 211Ea - St. Lawrence Glacial Marine Plain
EPA:
Level I: 8 - Eastern Temperate Forests
Level II: 8.1 - Mixed Wood Plains
Level III: 83 - Eastern Great Lakes Lowlands
Level IV: 83d - St. Lawrence Lowlands
83e - Upper St. Lawrence ValleyEcological 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 deep, coarse-loamy, and somewhat poorly drained soils that have formed in recent alluvium along streams where the stream gradient is controlled by bedrock. The soils formed in post-glacial alluvium derived predominantly from sandstone, dolomitic limestone, and less commonly gneiss and marble.
Vegetation Dynamics:
The reference community is a hardwood floodplain forest that is quite variable and very diverse depending on flood frequency and duration and depth to water table. Characteristic trees include silver maple, eastern cottonwood, ashes (green, white, black), red maple, box elder, sycamore, elms (American and slippery), hickories (shagbark, bitternut, shellbark), hackberry, sugar maple, tulip tree, and basswood. Characteristic shrubs include spicebush, winterberry, American hornbeam, bladdernut, speckled alder, shrubby dogwoods, viburnums, and sapling canopy trees. Characteristic vines include poison ivy, wild grapes, Virginia creeper, and virgin’s bower. Characteristic herbs include sensitive fern, jewelweeds, white snakeroot, wood nettle, false nettle, goldenrods, skunk cabbage, bluejoint grass, cutgrasses, and sedges (lakeside, bladder sedge, tussock, hop sedge).
Introduced trees such as black locust and white willow have become established in floodplains. Invasive non-native herbs include garlic mustard, moneywort, dame’s-rocket, European stinging nettle, and stiltgrass.Associated sites
F142XB002VT Dry Outwash
F142XB004VT Wet Outwash Depression
Similar sites
F142XA021NY Wet Till Depression
F142XB013NY Moist Till Upland
Table 1. Dominant plant species
Tree Not specified
Shrub Not specified
Herbaceous Not specified
Physiographic features
The site occurs on flood plains adjacent to low gradient streams and rivers. Slopes range from 0 to 3 percent.
Table 2. Representative physiographic features
Landforms (1) River valley > Flood plain
(2) Valley > Depression
Runoff class Negligible to very high Flooding duration Brief (2 to 7 days) Flooding frequency None to frequent Ponding frequency None to frequent Elevation 10 – 2998 ft Slope 0 – 8 % Water table depth 0 – 72 in 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, and snowfall is heavy from late in Autumn to early Spring. The frost-free period in this area is longest in a narrow belt around Lake Champlain.Table 3 Representative climatic features
Frost-free period (characteristic range) 110-130 days Freeze-free period (characteristic range) 140-150 days Precipitation total (characteristic range) 40-40 in Frost-free period (actual range) 110-140 days Freeze-free period (actual range) 130-160 days Precipitation total (actual range) 40-40 in Frost-free period (average) 120 days Freeze-free period (average) 150 days Precipitation total (average) 40 in Characteristic rangeActual rangeBarLineFigure 1. Monthly precipitation range
Characteristic rangeActual rangeBarLineFigure 2. Monthly minimum temperature range
Characteristic rangeActual rangeBarLineFigure 3. Monthly maximum temperature range
BarLineFigure 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) GOUVERNEUR 3 NW [USC00303346], Gouverneur, NY
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(2) LAWRENCEVILLE 3 SW [USC00304647], Nicholville, NY
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(3) OGDENSBURG 4 NE [USC00306164], Ogdensburg, NY
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(4) MASSENA INTL AP [USW00094725], Massena, NY
">Influencing water features
Poorly drained<br />
Water is removed so slowly that the soil is wet at shallow depths periodically during the growing season or remains wet for long periods. Internal free water occurrence is shallow or very shallow and common or persistent. Free water is commonly at or near the surface long enough during the growing season that most mesophytic crops cannot be grown, unless the soil is artificially drained. The soil, however, is not continuously wet directly below plow depth. Free water at shallow depth is common. The water table is commonly the result of low or very low saturated hydraulic conductivity, nearly continuous rainfall, or a combination of these. <br />
<br />
Very poorly drained<br />
Water is removed from the soil so slowly that free water remains at or very near the surface during much of the growing season. Internal free water occurrence is very shallow and persistent or permanent. Unless the soil is artificially drained, most mesophytic crops cannot be grown. The soils are commonly level or depressed and frequently ponded. In areas where rainfall is high or nearly continuous, slope gradients may be greater.Wetland description
National Wetland Classification (Cowardin et al., 1979):<br />
<br />
Palustrine, class variable, leaf morphology variable, water regime variable, chemistry modifier variable.Soil features
The site consists of deep, coarse-loamy, and somewhat poorly drained soils that have formed in recent alluvium along streams where the stream gradient is controlled by bedrock. Soil temperature regime is frigid. The representative soil map unit components are Cornish, Lovewell, Medomak, Ondawa, Podunk, Redwater, Rumney, and Sloan.
Table 4. Representative soil features
Parent material (1) Alluvium – gneiss
(2) Igneous, metamorphic and sedimentary rock
Surface texture (1) Fine sandy loam
(2) Sandy loam
(3) Loam
(4) Very fine sandy loam
Drainage class Very poorly drained to well drained Permeability class Very slow to moderate Depth to restrictive layer 50 – 72 in Soil depth 72 – 0 in Surface fragment cover <=3" Not specified Surface fragment cover >3" Not specified Available water capacity
(0-40in)0 – 13 in Soil reaction (1:1 water)
(0-40in)3.5 – 8.4 Subsurface fragment volume <=3"
(Depth not specified)0 – 34 % Subsurface fragment volume >3"
(Depth not specified)0 – 13 % Ecological dynamics
The information in this provisional ecological site description, including the state-and-transition model (STM), was developed using historical information, available data, professional experience, and scientific studies. The information is representative of a complex set of plant communities. Not all scenarios or plants are included. Key indicator plants, animals, and ecological processes are described to inform land management decisions.
Cultural Ecology: Humans have occupied the St. Lawrence River and Champlain Valley for at least ten thousand years, adapting their ways of life in a variety of changing environments. Initially people lived in small, nomadic groups and later in larger settlements. Historically, the area was within the Iroquois Tribal Territory. European exploration of the area began in the 17th century. Fur trade and settlement of the area followed during the 18th century. Industrialization, riverine-related activities, agriculture, concentrated human settlement in metropolitan areas, and recreation are currently the major human activities affecting the ecosystem (USDA USFS)
Natural Communities: The reference community is a hardwood floodplain forest (Edinger et al 2014) that is quite variable and very diverse depending on flood frequency and duration and depth to water table. Characteristic trees include silver maple, eastern cottonwood, ashes (green, white, black), red maple, box elder, sycamore, elms (American and slippery), hickories (shagbark, bitternut, shellbark), hackberry, sugar maple, tulip tree, and basswood. Characteristic shrubs include spicebush, winterberry, American hornbeam, bladdernut, speckled alder, shrubby dogwoods, viburnums, and sapling canopy trees. Characteristic vines include poison ivy, wild grapes, Virginia creeper, and virgin’s bower. Characteristic herbs include sensitive fern, jewelweeds, white snakeroot, wood nettle, false nettle, goldenrods, skunk cabbage, bluejoint grass, cutgrasses, and sedges (lakeside, bladder sedge, tussock, hop sedge).
Natural disturbances influencing the reference plant communities include flood frequency and duration, drought, insect damage, beaver activity, and tree falls. Introduced trees such as black locust and white willow have become established in floodplains. Invasive non-native herbs include garlic mustard, moneywort, dame’s-rocket, European stinging nettle, and stiltgrass.
The site has the potential to be converted in pastureland or cropland.
State and transition model
Custom diagramStandard diagram
Figure 7. Rich Floodplain State and Transition Model
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More interactive model formats are also available. View Interactive Models
Click on state and transition labels to scroll to the respective textEcosystem states
State 1 submodel, plant communities
142 PES Key 2
142 PES Key
1a. Soils frigid, shorter growing season (St. Lawrence Valley and Upper Champlain Valley)2a. Site periodically flooded during the growing season, adjacent to a river or stream [Medomak, Sloan, Redwater]...Low Floodplain F142XA001NY2b. Site not periodically flooded during the growing season, not adjacent to a river or stream3a. Substrate mostly organic (Histosols)4a. pH > 4.5; swamps and fens [Wonsqueak, Markey, Dorval]4b. pH < 4.5, bog [Wonsqueak, Loxley, Knob Lock, Dawson, Churubusco]3b. Substrate mostly mineral (Alfisols, Inceptisols, Spodosols, Entisols)5a. Parent material glacial outwash, soils coarse textured (sands) to moderately coarse textured (sandy loams)6a. Soils excessively drained to well drained7a. pH of upper 50 cm less than 5.5, low base saturation (acidic)8a. Soils shallow (< 50cm) to root restricting ortstein layer (iron cementation) [Constable, Wallace]8b. Soils very deep (>150cm) to bedrock [Stetson, Ondawa, Colosse, Adams, Melrose]7b. pH of upper 50 cm greater than greater than 5.5, higher base saturation (rich) [Missisquoi, Champlain, Waddington, Raquette, Trout River]6b. Soils moderately well drained to very poorly drained;9a. pH of upper 50 cm less than 5.5, low base saturation (acidic), watertable 25-100 cm deep (moderately well drained or somewhat poorly drained) [Lovewell, Occur, Coveytown, Duane, Au Gres, Wainola, Naumburg]9b. pH of upper 50 cm greater than 5.5, higher base saturation (rich)10a. Watertable 25-100 cm deep (moderately well drained or somewhat poorly drained) [Mooers, Sheddenbrook, Fahey, Flackville, Sciota, Northway, Eelweir]10b. Watertable <25 cm deep (poorly drained) [Searsport, Deinache, Stockholm, Cook, Coveytown, Deford, Munuscong, Pinconning]5b. Parent material glacial till or glaciolacustrine, soils coarse textured (sandy loams) to fine textured (clays)11a. Parent material glaciolacustrine, soils moderately coarse textured to fine textured12a. Soils well drained to somewhat poorly drained13a. pH of upper 50 cm less than 5.5, low base saturation (acidic) [Salmon, Nicholville]13b. pH of upper 50 cm greater than 5.5, higher base saturation (rich) [Buxton, Heuvelton, Depeyster, Elmwood, Muskellunge, Matoon, Hailsboro]12b. Soils poorly drained to very poorly drained [Adjidaumo, Guff, Wegatchie, Swanton, Whately]11b. Parent material glacial till, soils moderately coarse textured to medium textured14a. Soils poorly drained to very poorly drained) [Hannawa, Lyonmounten, Runeberg]14b. Soils excessively drained to somewhat poorly drained15a. pH of upper 50 cm less than 5.5, low base saturation (acidic)16a. Soils shallow and well drained to excessively drained (< 50cm) to bedrock [Ricker, Woodstock, Taconic, Success, Lyman, Hubbardton, Hogback, Irona, Insula, Quetico, Abram, Conic]16b. Soils shallow to very deep; somewhat poorly drained to well drained [Berkshire, Monadnock, Worth, Turnbridge, Rawsonville, Parishville, Mundalite, Millsite, Macomber, Gretor, Sunapee, Westbury, Skerry, Ampersand, Chazy, Topknot, Moira, Schroon]15b. pH of upper 50 cm greater than 5.5, higher base saturation (rich)17a. Soils shallow (< 50cm) to bedrock [Gouverneur, Summerville/Kings Falls]17b. Soils moderately deep to very deep (> 50cm) to bedrock or densic horizon18a. Soils well drained [Stowe, Marlow, Grenville, Pyrities, Nehasne, Neckrock, Galway cool]18b. Soils (moderately well drained or somewhat poorly drained) [Peru, Hogansburg, Kalurah, Ogdensburg, Malone, Brayton, Peasleeville]…Rich Moist Till Frigid F142XA020NY1b. Soils mesic, longer growing season (Eastern Ontario Plain and Lower Champlain Valley)19a. Substrate mostly organic (Histosols) [Aquents, Palms, Willette/Whallonsburg]19b. Substrate mostly mineral (Mollisol, Alfisols, Inceptisols, Spodosols, Entisols)20a. Landform a floodplain21a. Soils somewhat poorly to somewhat excessively drained…Reserved21b. Soils poorly or very poorly drained20b. Landform not a floodplain22a. Parent material glacial outwash, soils coarse textured (sands) to moderately coarse textured (sandy loams)23a. Soils poorly drained to very poorly drained [Scarboro, Rumney, Saco, Rippowam, Limerick, Gougeville, Enosburg]23b. Soils somewhat poorly drained to excessively drained24a. Soils well drained to excessively drained [Warwick, Tioga, Occum, Hamlin, Hadley, Kars, Factoryville, Hinesburg, Bonapart, Agawam, Arkport, Colonie, Copake, Grattan, Groton, Howard, Merrimac, Plainfield, Windsor]24b. Soils moderately well drained or somewhat poorly drained [Teel, Podunk, pootatuck, phelps, Lobdell, Herkimer, Castile, Wareham, Eldridge, Covertfalls, Northway, Cosad, Deerfield, Homer, Pipestone]22b. Parent material glacial till or glaciolacustrine, soils coarse textured (sandy loams) to fine textured (clays)25a. Parent material glaciolacustrine, soils medium textured to fine textured26a. Soils somewhat poorly drained to well drained27a. Soils fine to very fine texture (clay, clay loam, silty clay loam) [Vergennes, Wilpoint Cayuga, Hudson, Chaumont, Churchville, Kingsbury, Rhinebeck]27b. Soils coarse-silty, coarse loamy over clayey, sandy over clayey (silt loam, fine sandy loam, sandy loam, loamy fine sand) [Unadilla, Hartland, Belgrade, Claverack, Elmridge, Munson, Niagara, Stafford, Tonawanda]26b. Soils very poorly to poorly drained [Covington, Guffin, Binghamville, Livingston, Madalin, Panton]25b. Parent material glacial till, soils moderately coarse textured to medium textured28a. Soils excessively drained to well drained29a. pH of upper 50 cm less than 5.5, low base saturation (acidic)30a. Soils shallow to very shallow (< 50cm) to bedrock [Hollis, Galoo acid phase]30b. Soils moderately deep to very deep (> 50cm) to bedrock or densic horizon [Paxton, Charlton, Chatfield, Duchess, Lordstown, St. Albans]…Acidic Till Upland F142XB009VT29b. pH of upper 50 cm greater than 5.5, higher base saturation (rich)31a. Soils shallow to very shallow (< 50cm) to bedrock [Benson, Galoo, Farmington]31b. Soils moderately deep to very deep (> 50cm) to bedrock or densic horizon [Madrid, Nellis, Lowville, Galway, Gardenisle, Dover, Pittsfield, Stockbridge, Palatine, Farmington -moderately deep phase]28b. Soils moderately well drained to very poorly drained32a. Soils moderately well drained to somewhat poorly drained [Amenia, Angola, Bombay, Empeyville, Georgia, Kendaia, Massena, Newstead]32b. Soils poorly drained to very poorly drained33a. pH of upper 50 cm less than 5.5, low base saturation (acidic) [Ridgebury, Whitman]33b. pH of upper 50 cm greater than 5.5, higher base saturation (rich) [Lyons, Sun]State 1
Flood Plain ForestPlant species dominants: Silver maple - green ash- red maple-cottonwood/spicebush-winterberry-alders/sensitive fern.
Flood frequency, duration, and depth to water table are the primary factors influencing vegetation composition and change.Community 1.1
Late Successional (Mature) Floodplain ForestSilver Maple-Green Ash-Cottonwood/Spicebush/ Sensitive Fern.
Some characteristic community phase species are listed below.Community 1.2
Early to Mid Successional Community (Young Forest)Pathway 1.1A
Community 1.1 to 1.2Major flooding/river scouring. NRCS Practice 647 - Early successional Habitat Development/Management
Conservation practices
Early Successional Habitat Development/Management Pathway 1.2A
Community 1.2 to 1.1Minor flooding/river scouring/Succession/Time
Conservation practices
Forest Management Plan - Written State 2
Flood Plain Forest with Non-native SpeciesPlant species dominants: Silver maple-cottonwood-white willow-black locust/spicebush-shrub honeysuckles-multiflora rose/sensitive fern-garlic mustard.
Native forest species are associated with various non-native and potentially invasive species.State 3
PasturelandThe pastureland state is suitable for livestock grazing or as hayland. Adapted forage species for beef pasture include Ladino white clover, Kentucky bluegrass, Timothy, orchardgrass, and tall fescue (Cornell University).
State 4
CroplandThe cropland state is suitable for either perennial or annual crops. Common commodities include grains, oilseeds, dry beans, dry peas, tobacco, cotton, fruits, tree nuts, berries, and cut Christmas trees.
Transition TIA
State 1 to 2Anthropogenic disturbance and non-native seed dispersal.
Transition T1B
State 1 to 3NRCS Practices: 460 - Land Clearing; 466 - Land Smoothing
Transition T1C
State 1 to 4NRCS Practices: 460 - Land Clearing; 466 - Land Smoothing
Restoration pathway R2A
State 2 to 1Conservation practices
Brush Management Restoration and Management of Rare and Declining Habitats Invasive Plant Species Control Forest Management Plan - Applied Herbaceous Weed Control Transition T2A
State 2 to 3NRCS Practices: 460 - Land Clearing; 466 - Land Smoothing
Transition T2B
State 2 to 4NRCS Practices: 460 - Land Clearing; 466 - Land Smoothing
Restoration pathway R3A
State 3 to 1Conservation practices
Tree/Shrub Establishment Restoration and Management of Rare and Declining Habitats Native Plant Community Restoration and Management Transition T3A
State 3 to 4Crop establishment
Restoration pathway R4A
State 4 to 1Conservation practices
Tree/Shrub Establishment Restoration and Management of Rare and Declining Habitats Native Plant Community Restoration and Management Additional community tables
Table 5. Community 1.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Table 6. Community 1.1 forest overstory composition
Common name Symbol Scientific name Nativity Height ft Canopy cover (%) Diameter in Basal area (square ft/acre) Treeslippery elm ULRU Ulmus rubra Native – – – 0 bitternut hickory CACO15 Carya cordiformis Native – – – 0 shagbark hickory CAOV2 Carya ovata Native – – – 0 shellbark hickory CALA21 Carya laciniosa Native – – – 0 eastern cottonwood PODE3 Populus deltoides Native – – – 0 white ash FRAM2 Fraxinus americana Native – – – 0 green ash FRPE Fraxinus pennsylvanica Native – – – 0 black ash FRNI Fraxinus nigra Native – – – 0 red maple ACRU Acer rubrum Native – – – 0 boxelder ACNE2 Acer negundo Native – – – 0 silver maple ACSA2 Acer saccharinum Native – – – 0 common hackberry CEOC Celtis occidentalis Native – – – 0 sugar maple ACSA3 Acer saccharum Native – – – 0 tuliptree LITU Liriodendron tulipifera Native – – – 0 American basswood TIAM Tilia americana Native – – – 0 American sycamore PLOC Platanus occidentalis Native – – – 0 American elm ULAM Ulmus americana Native – – – 0 Table 7. Community 1.1 forest understory composition
Common name Symbol Scientific name Nativity Height (ft) Canopy cover (%) Forb/Herbwhite snakeroot AGAL5 Ageratina altissima Native – – Canadian woodnettle LACA3 Laportea canadensis Native – – smallspike false nettle BOCY Boehmeria cylindrica Native – – jewelweed IMCA Impatiens capensis Native – – Fern/fern allysensitive fern ONSE Onoclea sensibilis Native – – Shrub/Subshrubnorthern spicebush LIBE3 Lindera benzoin Native – – common winterberry ILVE Ilex verticillata Native – – speckled alder ALINR Alnus incana ssp. rugosa Native – – American bladdernut STTR Staphylea trifolia Native – – redosier dogwood COSE16 Cornus sericea Native – – southern arrowwood VIDE Viburnum dentatum Native – – Vine/Lianaeastern poison ivy TORA2 Toxicodendron radicans Native – – Virginia creeper PAQU2 Parthenocissus quinquefolia Native – – Table 8. Community 1.2 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Interpretations
Supporting information
Inventory data references
Future work is needed, as described in a future 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
Cornell University. 2018. Forage Species Selection Tool. Accessed in 2018: http://forages.org
Edinger, G. J., D. J. Evans, S. Gebauer, T. G. Howard, D. M. Hunt, and A. M. Olivero (editors). 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.
USDA-NASS. 2012 Census of Agriculture. St. Lawrence County New York. Accessed on 11/17/17: https://www.agcensus.usda.gov/Publications/2012/Online_Resources/County_Profiles/New_York/cp36089.pdf
USDA-USFS. Ecological Subregions of the United States. 212E--St. Lawrence and Champlain Valley. Northeastern Forest Experiment Station, Northeastern Area State and Private Forestry, and the Eastern Region. Accessed on 11/17/17: https://www.fs.fed.us/land/pubs/ecoregions/ch14.html#212EContributors
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 09/22/2026 Approved by Approval date Composition (Indicators 10 and 12) based on Annual Production Indicators
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Number and extent of rills:
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Presence of water flow patterns:
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Number and height of erosional pedestals or terracettes:
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Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
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Number of gullies and erosion associated with gullies:
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Extent of wind scoured, blowouts and/or depositional areas:
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Amount of litter movement (describe size and distance expected to travel):
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Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
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Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
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Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
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Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on this site):
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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:
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Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
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Average percent litter cover (%) and depth ( in):
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Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
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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:
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Perennial plant reproductive capability:
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