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Ecological site R238XY409AK
Arctic Dwarf Scrub-Lichen Sandy Soil
Last updated: 9/29/2026
Accessed: 10/07/2026
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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): 238X–Yukon-Kuskokwim Coastal Plain
Geography
The Yukon-Kuskokwim Coastal Plain area (MLRA 238X) consists of the broad, nearly level delta along the lower reaches of the Yukon and Kuskokwim rivers, where the rivers empty into the Bering Sea. The Yukon River runs along the northern edge of the area while the Kuskokwim River runs along the southern edge. This MLRA makes up 31,565 square miles. MLRA 238x is bordered by MLRA 240X (Nulato Hills-Southern Seward Peninsula Highlands) to the North, MLRA 237X (Ahklun Mountains) to the South, and MLRAs 230X (Yukon-Kuskokwim Highlands) and 229X(Interior Alaska Lowlands) to the East. Although the MLRA is mostly undeveloped wild land and is sparsely populated, there are 42 villages scattered along the coast or the banks of the Yukon and Kuskokwim Rivers. The principal communities are Aniak, Bethel, Emmonak, Hooper Bay, and Saint Mary’s.
Physiography
Although primarily comprised of deltaic lowlands, in a few areas, isolated low hills rise above the surrounding coastal plain. Numerous low-gradient streams meander through this MLRA, many of which are tributaries or former channels of the Yukon and Kuskokwim Rivers. Depressions and shallow basins on the coastal plain are dotted with interconnecting stream channels, wetlands, and countless small and medium-size lakes. On the floodplains between channels and wetlands, low escarpments, meander scars, oxbow lakes, sloughs, and islands can be found. The coastline is broken by several large inlets and bays, including Baird Inlet, which forms a large inland sea behind Nelson Island.
Elevations generally range from sea level to 300 feet but reach heights of 2,342 feet at the summit of Towak Mountain. A vast majority of the surface water from interior and western Alaska drains into the Bering Sea through MLRA 238x. Major rivers include the Yukon, Kuskokwim, Tovers, Black, Azun, Kashunuk, and Izaviknek Rivers. In addition to the various rivers and tributaries, lakes make up about 40 percent of this MLRA. This area is in the zone of discontinuous permafrost, where permafrost is thin to moderately thick and primarily occurs in fine textured soils. Permafrost does not generally occur on flood plains or in areas near bodies of water.
Geology
MLRA 238x was unglaciated during the Pleistocene, except for along the southern edge, where glaciers from the Ahklun mountains may have extended into portions of the lowlands. A majority of the sediments across the area are fine textured Holocene and Pleistocene deltaic deposits from the Yukon and Kuskokwim Rivers, and loamy and sandy Holocene fluvial deposits on flood plains and stream terraces. In the western part of the MLRA, low basalt hills, cinder cones, and volcanic craters from the Cretaceous and Tertiary can be found.
Climate
The climate of MLRA 238x is primarily maritime throughout the summer, and when Bering Sea ice pack forms in the winter, it becomes more characteristic of a continental climate. Summers are short, cloudy, and rainy while winters are long, cold, and foggy, especially in coastal areas. Windy conditions are common throughout the year. Mean annual precipitation is 12 to 30 inches and mean annual snowfall ranges from 40 to 90 inches. Freeze-free period range 116 to 150 days, but freezing temperatures can occur year-round, although rare in June, July, and August. This cold climate leads to MLRA 238X being included in the Arctic.
Soils
The dominant soil orders in MLRA 238X are Gelisols, Histosols, Inceptisols, and Entisols. Soils have a subgelic or cryic temperature regime, and an aquic or udic moisture regime. Fibristels, Hemistels, Histoturbels, and Aquiturbels are the most common Gelisol great groups. Fibristels and Hemistels have thick accumulations of organic material and occur in depressions and shallow basins. The Orthels and Turbels have comparably thinner surface organic material. The Histoturbels are common in elevated and convex areas and Aquiturbels are common on terraces and drainageways. Inceptisols, Entisols, and Histosols do not have permafrost within the soil profile. Histosols occur in depressions with thick accumulations of organic material. Inceptisols occur on the slopes of hills and mountains, swales, terraces, and flood plains. Entisols occur on shore complex and flood plains.
Vegetation
Lakes, ponds, and other types of surface water are common in this area and vegetation near these water bodies include wet sedge meadows, sedge-shrub meadows, and sedge-moss meadows. Low uplands support low and dwarf ericaceous shrubs, tussock-forming sedges, other hydrophytic plants, and mosses. Sites with higher local relief and better drainage support low ericaceous scrub with mosses, lichens, willows, and forbs. Low ericaceous shrubs, willow, alder, and mosses are understory associated in these forests and woodlands.
Land use
Residents use this area primarily for subsistence hunting, fishing, and gathering. Less than one percent of the MLRA is urban, and most communities are along the coast or major rivers and lakes. Disturbance of fragile permafrost soils is the major soil resource concern in this area, resulting from damage of insulating organic material that allows permafrost in upper soil layers to thaw. This can lead to ponding, soil subsidence, erosion, and altered hydrologic function. In order to slow the thawing of permafrost, management is needed to protect organic material and promote thermal balance of soils.Classification relationships
Landfire Biophysical Settings:
6716840 - Alaska Arctic Mesic Sedge-Dryas Tundra
(LANDFIRE , 2009)
Viereck Communities:
Level 3 - III.C.2 - Lichen
Level 4 - III.C.2.b - Foliose and Fruticose Lichen
(Viereck et al., 1992)Ecological site concept
This ecological site:
• occurs on non-coastal, sandy soils on the Yukon-Kuskokwim delta plain
• supports a mix of foliose lichens with dwarf scrubs (some stable areas on protected slopes of dunes and relict lake beds support an alder community)
• is associated with sandy soils
• is prone to wind erosion and blow outs, exposing areas of open sandAssociated sites
R238XY404AK Arctic Loamy Frozen Tussock Tundra
R238XY404AK describes the tussock-scrub tundra underlain by near-surface permafrost.
Similar sites
R238XY402AK Arctic Scrub Hills and Mountains Complex
R238XY402AK describes Dryas dwarf scrublands on hill and mountain slopes along the borders of MLRA 238. Soils are loess or ash over colluvium or till and rock fragments are present in the subsurface horizons.
Table 1. Dominant plant species
Tree Not specified
Shrub (1) Empetrum nigrum
(2) Betula nanaHerbaceous (1) Alectoria nigricans
(2) Bryocaulon divergensPhysiographic features
This ecological site occurs on sandy soils on dunes and dried relict lake beds. These landforms are minor but widespread across the upland delta plains. Flooding and ponding do not occur. A water table is generally present between 20 and 39 inches throughout the growing season.
Table 2. Representative physiographic features
Geomorphic position, hills (1) Crest
Geomorphic position, flats (1) Dip
Slope shape across (1) Convex
(2) Linear
Slope shape up-down (1) Linear
Landforms (1) Delta plain > Dune
(2) Delta plain > Relict lakebed
Runoff class Low to medium Flooding frequency None Ponding frequency None Elevation 30 – 50 ft Slope 1 – 7 % Water table depth 20 – 39 in Aspect W, NW, N, NE, E, SE, S, SW Table 3. Representative physiographic features (actual ranges)
Runoff class Low to medium Flooding frequency None Ponding frequency None to rare Elevation 10 – 80 ft Slope 0 – 12 % Water table depth 0 – 60 in Climatic features
Sea ice strongly influences the climate of MLRA 238X, as it does throughout Western Alaska. The climate is characteristically maritime throughout the summer months, where cool, moist air moves from the Bering Sea into coastal lowlands. As sea ice forms in the winter, the climate becomes more characteristic of a continental climate. These cold year-round conditions is the reason MLRA 238X is considered Arctic despite being approximately 500 miles south of the Arctic circle.
Winters are cold and long, with average low temperatures between 0 and 4 degrees (F) December through February. Winter and early spring is the driest time of the year with less than an inch of precipitation per month falling January through April. Summers in this area are cool, short, and often cloudy and rainy. June through October are considerably wetter, with the most precipitation falling in August and September.Table 4 Representative climatic features
Frost-free period (characteristic range) 90 days Freeze-free period (characteristic range) 120 days Precipitation total (characteristic range) 20 in Frost-free period (actual range) 90 days Freeze-free period (actual range) 120 days Precipitation total (actual range) 20 in Frost-free period (average) 90 days Freeze-free period (average) 120 days Precipitation total (average) 20 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) BETHEL AP [USW00026615], Bethel, AK
">Influencing water features
This ecological site is not associated with water features. When found in relict lake beds, this ecological site is dry and no longer floods or ponds. Precipitation and ground water are the main sources of water.
Soil features
• Soils formed in sandy eolian deposits.
• Rock fragments do not occur on the soil surface or in the soil profile.
• Mineral soils are capped with an organic horizon of two to four inches.
• Soils are very deep. Near-surface permafrost is generally absent, but may be present in ecotonal areas where this ecological site abuts a true permafrost soil, such as the cottongrass tundra (R238XY404AK)
• Soil pH ranges from extremely to slightly acidic.
• Soils are primarily moderately well or well drained. Alder communities are usually poorly drained and have a perched, shallow water table atop seasonal ice.Table 5. Representative soil features
Parent material (1) Eolian sands
(2) Eolian deposits
Surface texture (1) Very fine sandy loam
(2) Loamy fine sand
(3) Fine sand
Family particle size (1) Sandy
Drainage class Moderately well drained to well drained Permeability class Moderate to rapid Depth to restrictive layer 60 – 0 in Soil depth 79 – 0 in Surface fragment cover <=3" Not specified Surface fragment cover >3" Not specified Available water capacity
(0-10in)0.6 – 1.6 in Soil reaction (1:1 water)
(0-10in)4.1 – 6 Subsurface fragment volume <=3"
(Depth not specified)Not specified Subsurface fragment volume >3"
(Depth not specified)Not specified Table 6. Representative soil features (actual values)
Drainage class Poorly drained to well drained Permeability class Moderate to rapid Depth to restrictive layer 16 – 0 in Soil depth 79 – 0 in Surface fragment cover <=3" 0 % Surface fragment cover >3" 0 % Available water capacity
(0-10in)0 – 3.2 in Soil reaction (1:1 water)
(0-10in)4.1 – 6 Subsurface fragment volume <=3"
(Depth not specified)0 % Subsurface fragment volume >3"
(Depth not specified)0 % Ecological dynamics
The Yukon-Kuskokwim Coastal Plain MLRA has a harsh climate and cold soils in the zone of discontinuous permafrost. This MLRA occurs in the arctic biome and has a growing season that is both short and cold. As a result, the vertical and horizontal structure of vegetation is severely limited. Vegetation within the arctic biome is typically restricted to dwarf shrubs, mosses, and lichens.
This ecological site describes sandy soils on dunes and in relict lake beds. These landforms are generally small but repeatable across the delta plains uplands. Soil and site hydrology are influenced by the sandy soil, which in turns supports a unique reference plant community. This ecological site supports a lichen-dwarf shrub reference plant community.
Erosion is the major influencing factors supporting three communities on this ecological site. Removal of surface biomass via plant dieback or natural disturbance (wind, fire, lichen grazing by caribou) exposes the sandy subsurface soil. Once the stabilizing surface biomass and underlying roots are removed, the soil becomes more prone to erosion and may result in a full blowout of the dune. This unvegetated area is described by community 1.2. Soil erosion is a relatively common disturbance on these exposed slopes. However, there are locations where the effects of wind erosion are diminished, such as along relict lake bed edges and on the leeward side of dune crests. When these conditions develop along with a perched shallow water table atop seasonal ice, a stable closed alder community develops, represented by community 1.3.
There is evidence of historical fire in this ecological site. Charcoal can be found in the soil profile where fire has occurred. While fuel load is generally very low, the lichen-dwarf shrub community may catch fire from lightning ignition. Human activity can damage and remove the vegetation, creating a non-vegetated sandy berm susceptible to further wind erosion. If left to recover, the reference plant community will generally reestablish.
The information in this Ecological Dynamics section, including the state-and-transition model (STM), was developed based on current field data, professional experience, and a review of the scientific literature. As a result, all possible scenarios or plant species may not be included. Key indicator plant species, disturbances, and ecological processes are described to inform land management decisions.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 textEcosystem states
SWAPAEHState 1 submodel, plant communities
1.1a - Erosion 1.1b - Autogenic succession on stable, wetter soils 1.2a - Autogenic succession 1.3a - Erosion State 1
Reference StateThe reference state supports three community phases, grouped by the structure and dominance of the vegetation (e.g., shrubs and lichens) and their ecological function and stability. The reference plant community is characterized by a closed lichen-dwarf shrub community. The presence of this and related communities are dictated temporally and spatially by the presence of sandy soils, water table depth, and dune erosion. All community phases in this report are characterized using the Alaska vegetation classification system (Viereck et al., 1992).
Resilience management. This ecological site and the communities within it are very susceptible to wind erosion. Natural disturbances that remove the vegetation, such as wind, fire, and grazing, create a positive feedback loop of continued wind erosion. Disturbances from ATVs and snowmachines act in the same way.
Dominant plant species
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black crowberry (Empetrum nigrum), shrub
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dwarf birch (Betula nana), shrub
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marsh Labrador tea (Ledum palustre ssp. decumbens), shrub
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bog blueberry (Vaccinium uliginosum), shrub
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Bigelow's sedge (Carex bigelowii), grass
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witch's hair lichen (Alectoria nigricans), other herbaceous
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(Flavocetraria cucullata), other herbaceous
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reindeer lichen (Cladina mitis), other herbaceous
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reindeer lichen (Cladina stygia), other herbaceous
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bryocaulon lichen (Bryocaulon divergens), other herbaceous
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greygreen reindeer lichen (Cladina rangiferina), other herbaceous
Dominant resource concerns
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Wind erosion
Community 1.1
Black crowberry - Dwarf birch / Witch's hair lichen - Bryocaulon lichen
Figure 7. The dune landform is generally a broad, convex slope that stands out against the surrounding tundra landscape.
The reference plant community is a lichen-dwarf scrub community (Viereck et al., 1992). It is on sandy soils, prevalent on dunes and in relict lake beds. This community is usually easily recognizable by the large mounds of dark bryocaulon lichen. Major plant groups are lichens and dwarf shrubs. Common species include black crowberry, dwarf birch, marsh Labrador tea, bog blueberry, witch's hair lichen, reindeer lichens, and bryocaulon lichen. Ground cover is typically comprised of herbaceous litter, moss, and bare soil.
Resilience management. This community has medium resilience unless the surface and subsurface biomass is disturbed. Small disturbances that damage the lichens, such as selective grazing and ATV riding, will expose the sandy soil which is easily erodible.
Dominant plant species
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black crowberry (Empetrum nigrum), shrub
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dwarf birch (Betula nana), shrub
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marsh Labrador tea (Ledum palustre ssp. decumbens), shrub
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bog blueberry (Vaccinium uliginosum), shrub
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Bigelow's sedge (Carex bigelowii), grass
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witch's hair lichen (Alectoria nigricans), other herbaceous
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(Flavocetraria cucullata), other herbaceous
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bryocaulon lichen (Bryocaulon divergens), other herbaceous
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reindeer lichen (Cladina stygia), other herbaceous
Dominant resource concerns
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Wind erosion
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Organic matter depletion
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Naturally available moisture use
Figure 8. Annual production by plant type (representative values) or group (midpoint values)
Community 1.2
Moss / Lichen / Dwarf Shrub Dune Blow Out
Figure 9. Dune blow outs present in a variety of ways, but generally consist of an open sandy area with eroding edges.
This community is mostly bare, exposed soil. Colonizing species are usually present. Surviving dwarf shrubs colonize from edges, while windblown fragments of lichen and moss are generally the first species colonizing the center of blow outs. Ground cover is typically bare, sandy soil and drift wood.
Dominant plant species
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black crowberry (Empetrum nigrum), shrub
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Lichen (Lichen), other herbaceous
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Moss (Moss), other herbaceous
Figure 10. Annual production by plant type (representative values) or group (midpoint values)
Table 7. Ground cover
Tree foliar cover 0% Shrub/vine/liana foliar cover 0-10% Grass/grasslike foliar cover 0% Forb foliar cover 0% Non-vascular plants 0-10% Biological crusts 0% Litter 0-0% Surface fragments >0.25" and <=3" 0% Surface fragments >3" 0% Bedrock 0% Water 0% Bare ground 80-100% Table 8. Soil surface cover
Tree basal cover 0% Shrub/vine/liana basal cover 0% Grass/grasslike basal cover 0% Forb basal cover 0% Non-vascular plants 0-10% Biological crusts 0% Litter 0-0% Surface fragments >0.25" and <=3" 0% Surface fragments >3" 0% Bedrock 0% Water 0% Bare ground 90-100% Community 1.3
Sitka alder - Spirea / Clubmoss - Woodfern
Figure 11. The alder community can develop on the leeward (wind-protected) side of dune crests above the tundra landscape.
Figure 12. The same protected conditions that stabilize the sandy soil also allow snow to accumulate. This provides water later through the growing season than a typical sandy soil.
This community occurs on wetter soils that have been stabilized for a long period of time. These soils are most common along relict lake bed edges and leeward side of steep dunes, where wind erosion is less and snow pack lasts longer into the growing season. This community is a closed tall alder scrubland (Viereck et al., 1992). Major plant groups are tall and medium shrubs, and medium and low forbs. Common species include Sitka alder, spirea, clubmoss, and woodfern. Ground cover is typically comprised of herbaceous litter.
Resilience management. This community develops in protected areas out of the wind. It is very resilient to natural, regularly occurring disturbances.
Dominant plant species
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Sitka alder (Alnus viridis ssp. sinuata), shrub
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beauverd spirea (Spiraea stevenii), shrub
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stiff clubmoss (Lycopodium annotinum), other herbaceous
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spreading woodfern (Dryopteris expansa), other herbaceous
Figure 13. Annual production by plant type (representative values) or group (midpoint values)
Pathway 1.1a
Community 1.1 to 1.2
Black crowberry - Dwarf birch / Witch's hair lichen - Bryocaulon lichen
Moss / Lichen / Dwarf Shrub Dune Blow OutThe loss of surface biomass exposes the sandy surface to wind erosion. Lichens do not root and may be removed via wind, fire, or grazing. Shrubs are generally more hardy and their roots hold the sandy soil in place. However, the same disturbances may kill roots. Subsequent wind erosion results in a blow out.
Context dependence.A small loss of biomass can result in a positive feedback loop of continuing wind erosion.
Key drivers
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Wildlife grazing or browsing
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Fire
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Mechanical soil disturbance
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Wind erosion
Key ecosystem services affected
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Erosion control
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Primary production
Pathway 1.1b
Community 1.1 to 1.3
Black crowberry - Dwarf birch / Witch's hair lichen - Bryocaulon lichen
Sitka alder - Spirea / Clubmoss - WoodfernThe sandy soils are particularly stable and wetter in areas such as relict lake edges and on leeward slopes of dunes. In these areas, the time between major erosion events is generally longer. As the overstory develops in an undisturbed area, herbaceous litter and summer shading cool temperatures and seasonal ice persists longer into the growing season. The seasonal ice perches water, creating a positive feedback loop where readily available water increases and supports slower growing, taller shrubs.
Key ecosystem services affected
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Erosion control
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Nutrient cycling
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Primary production
Pathway 1.2a
Community 1.2 to 1.1
Moss / Lichen / Dwarf Shrub Dune Blow Out
Black crowberry - Dwarf birch / Witch's hair lichen - Bryocaulon lichenColonization of bare sandy soil requires dune stabilization. If erosion continues, the dune will continue to be exposed. Colonization by wind-blown seeds and moss and lichen fragments occurs throughout the sandy blowout. Shrub encroachment occurs around the blow out edges.
Pathway 1.3a
Community 1.3 to 1.2
Sitka alder - Spirea / Clubmoss - Woodfern
Moss / Lichen / Dwarf Shrub Dune Blow OutThe loss of vegetation exposes the sandy surface to wind erosion. Unlike in community 1.1, a major disturbance is generally required, such as fire or alder dieback. Wind erosion results in a dune blow out.
Additional community tables
Table 9. Community 1.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Lichen1 Lichens – witch's hair lichen ALNI60 Alectoria nigricans – 0–40 bryocaulon lichen BRDI60 Bryocaulon divergens – 0–30 reindeer lichen CLMI60 Cladina mitis – 0–15 reindeer lichen CLST5 Cladina stygia – 0–15 greygreen reindeer lichen CLRA60 Cladina rangiferina – 0–15 witch's hair lichen ALOC60 Alectoria ochroleuca – 0–10 FLCU Flavocetraria cucullata – 2–10 star reindeer lichen CLST60 Cladina stellaris – 0–10 snow lichen STERE2 Stereocaulon – 0–2 Shrub/Vine2 Shrubs – black crowberry EMNI Empetrum nigrum – 10–25 bog blueberry VAUL Vaccinium uliginosum – 0–25 dwarf birch BENA Betula nana – 15–20 marsh Labrador tea LEPAD Ledum palustre ssp. decumbens – 10 alpine azalea LOPR Loiseleuria procumbens – 0–4 lingonberry VAVI Vaccinium vitis-idaea – 0–2 alpine bearberry ARAL2 Arctostaphylos alpina – 0–2 Grass/Grasslike3 Graminoids – Bigelow's sedge CABI5 Carex bigelowii – 1–5 Table 10. Community 1.2 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Lichen1 Lichens – bryocaulon lichen BRDI60 Bryocaulon divergens – 5–20 snow lichen STERE2 Stereocaulon – 3–8 FLCU Flavocetraria cucullata – 3–7 witch's hair lichen ALNI60 Alectoria nigricans – 2–5 witch's hair lichen ALOC60 Alectoria ochroleuca – 2–5 reindeer lichen CLMI60 Cladina mitis – 1–3 reindeer lichen CLST5 Cladina stygia – 0–2 FLNI Flavocetraria nivalis – 0–2 Moss2 Mosses – Moss 2MOSS Moss – 5–10 racomitrium moss RALA70 Racomitrium lanuginosum – 3–8 polytrichum moss POLYT5 Polytrichum – 2–5 dicranum moss DICRA8 Dicranum – 0–2 Shrub/Vine3 Shrubs – black crowberry EMNI Empetrum nigrum – 5–15 alpine azalea LOPR Loiseleuria procumbens – 3–7 dwarf birch BENA Betula nana – 1–3 alpine bearberry ARAL2 Arctostaphylos alpina – 0–2 Table 11. Community 1.3 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Shrub/Vine1 Shrubs – Sitka alder ALVIS Alnus viridis ssp. sinuata – 40–80 beauverd spirea SPST3 Spiraea stevenii – 10–50 lingonberry VAVI Vaccinium vitis-idaea – 0–10 Grass/Grasslike2 Graminoids – Graminoid (grass or grass-like) 2GRAM Graminoid (grass or grass-like) – 0–20 Forb3 Forbs – stiff clubmoss LYAN2 Lycopodium annotinum – 0–70 spreading woodfern DREX2 Dryopteris expansa – 0–7 false toadflax GELI2 Geocaulon lividum – 0 Moss4 Mosses – sphagnum SPHAG2 Sphagnum – 10–40 Moss 2MOSS Moss – 0 Interpretations
Supporting information
Inventory data references
Vegetative communities and transitions are described using NRCS Soil-VegPlot correlated field data, existing models, and expert knowledge. External data sources: The Alaska Vegetation Classification (Viereck et al., 1992) The Alaska-Yukon Region of the Circumboreal Vegetation Map (CBVM) (Jorgensen and Meidinger, 2015) LANDFIRE Biophysical Settings Models (Landfire, 2009)
References
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Viereck, L.A., C. T. Dyrness, A. R. Batten, and K. J. Wenzlick. 1992. The Alaska vegetation classification. U.S. Department of Agriculture, Forest Service, Pacific Northwest Forest and Range Experiment Station General Technical Report PNW-GTR-286..
Other references
Landfire. 2009. Biophysical Setting. 6716840 - Alaska Arctic Mesic Sedge-Dryas Tundra. In: LANDFIRE National Vegetation Dynamics Models. USDA Forest Service and US Department of Interior. Washington, DC.
United State Department of Agriculture. 2008. Hydrogeomorphic Wetland Classification System: an overview and modification to better meet the needs of the Natural Resources Conservation Service. Technical note No 190-8-76.
United States Department of Agriculture, Natural Resources Conservation Service (USDA-NRCS). 2022. Land resource regions and major land resource areas of the United States, the Caribbean, and the Pacific Basin. U.S. Department of Agriculture, Agriculture Handbook 296.Contributors
Marji Patz, Regional Ecological Site Specialist
Phil Barber, Ecologist
Abbie Clapp, Soil ScientistApproval
Jamin Johanson, 9/29/2026
Acknowledgments
This ecological site was developed to describe soils mapped around Nunapitchuk, AK during the AK705 - YK Delta Village Mapping project. Field work was conducted in March and June of 2026. Field staff from the Homer, Wasilla, and Fairbanks field offices contributed to the data collection allowing for this ecological site and associated soils to be described.
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 10/07/2026 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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