

Natural Resources
Conservation Service
Ecological site F220XY432AK
Maritime Forest Gravelly Plain
Last updated: 3/10/2025
Accessed: 03/31/2025
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): 220X–Alexander Archipelago-Gulf of Alaska Coast
The Alexander Archipelago-Gulf of Alaska Coast area consists of a narrow arc of islands and lower elevation coastal mountains in the Southern Alaska Region. This area spans from the Alexander Archipelago in southeastern Alaska, north and west along the coast of the Gulf of Alaska and Prince William Sound, and further west to the southern tip of the Kenai Peninsula and the northeastern islands of the Kodiak Archipelago. The area makes up about 27,435 square miles (USDA 2006). The terrain primarily consists of low to moderate relief mountains that are deeply incised. Throughout the area glaciers, rivers, and streams have cut deep, narrow to broad valleys. The broader valleys have nearly level to strongly sloping flood plains and stream terraces. Alluvial and colluvial fans and short footslopes are common in the valleys along the base of the mountains. Rocky headlands, sea cliffs, estuaries, and beaches are common along the coast.
This area includes the Municipality of Juneau, Alaska's capital, and a number of smaller coastal towns and villages. Federally administered lands within this MLRA include Admiralty Island National Monument and part of Misty Fjords National Monument, Tongass National Forest, Chugach National Forest, and Glacier Bay, Wrangell-St. Elias, and Kenai Fjords National Parks and Preserves. The southern terminus of the Trans-Alaska Pipeline is in Valdez.
During the late Pleistocene epoch, the entire area was covered with glacial ice. The numerous fjords of the Alexander Archipelago and Prince William Sound were formed chiefly as a result of glacial scouring and deepening of preglacial river valleys. Most glacial deposits have been eroded away or buried by mountain colluvium and alluvium, which cover about 90 percent of the present landscape. The remaining glacial and glaciofluvial deposits are generally restricted to coastal areas. During the Holocene epoch, volcanic activity within and adjacent to this area deposited a layer of volcanic ash of varying thickness on much of the landscape in the southeastern and northwestern parts of the area. Paleozoic, Mesozoic, and Lower Tertiary stratified sedimentary rocks and Cretaceous and Tertiary intrusive rocks underlie much of the area and are exposed on steep mountain
slopes and ridges (USDA 2006).
The dominant soil orders in this MLRA are Spodosols, Histosols, and Entisols. Soils in the area typically have a cryic soil temperature regime, an udic moisture regime, and have mixed minerology. Spodosols are common on mountains and hills having been formed in gravelly or cobbly colluvium, glacial till, and varying amounts of silty volcanic ash. These Spodosols commonly range from shallow to deep, are well to somewhat poorly drained, and typically classify as Humicryods or Haplocryods. Histosols that are poorly to very poorly drained occur on footslopes, discharge slopes, and valley floors. These wet histosols commonly classify as Cryosaprists, Cryohemists, and Cryofibrists. Histosols that are well drained occur on steep mountainsides. These dry Histosols commonly classify as Cryofolists. Entisols are common on flood plains, stream terraces, and outwash plains having been formed in silty, sandy, and gravelly to cobbly alluvium. These Entisols are generally deep, range from well to somewhat poorly drained, and commonly classify as Cryaquents and Cryofluvents. Miscellaneous (non-soil) areas make up about 23 percent of the MLRA. The most common miscellaneous areas are avalanche chutes, rock outcrop, rubble land, beaches, river wash, and water.
This area represents the northern extent of the Pacific temperature rainforest and is characterized by productive stands of conifers. Western hemlock and Sitka spruce are the dominant trees on mountains and hills at the lower elevations. Due to warmer temperatures, western red cedar and Alaska cedar are more prevalent in the southern part of the area. Black cottonwood and mixed forest types occur on flood plains. Areas of peat and other sites that are too wet for forest growth support sedge-grass meadows and low scrub. The transition to subalpine and alpine communities typically occurs at elevations between 1500 to 3000 feet (Boggs et al. 2010, Carstensen 2007, Martin et al. 1995), which characterize the vegetation of the Southern Alaska Coastal Mountains area.
For many decades, logging, commercial fishing, and mining have been the primary industrial land uses throughout much of the area. In recent years, changes in public interests, land use policies, and timber economics have contributed to a significant decline in the timber industry. Commercial fishing continues to be an important industry and most communities support a fleet of boats and fishing related facilities. A number of mines operate in the area and others have been prospected and proposed. Tourism and wildland recreation are becoming increasingly important. Subsistence hunting, fishing, and gathering provide food and a variety of other resources to local residents and remain the principal economy for residents of remote villages.
Ecological site concept
This site occurs on outwash plains, outwash deltas, and glacial valley floors. Flooding is very rare and ponding is not known to occur on these well drained soils. The soil texture is sandy to loamy-skeletal and a water table is typically greater than 20 inches year-round. This site occurs at elevations from sea level to 330 feet, and slopes are typically 0-20%.
Five plant communities occur on this site and are a function of primary succession coupled with disturbance dynamics driven by windthrow events. The reference plant community phase is characterized as open needleleaf spruce forest. It is composed primarily of mature Sitka spruce and western hemlock with an extensive feathermoss understory. Common understory species include Sitka alder, oval-leaf blueberry, strawberryleaf raspberry, sidebells wintergreen, heartleaf twayblade, western rattlesnake plantain, stairstep moss, Schreber’s big red stem moss, and goose neck moss.
Associated sites
F220XY435AK |
Maritime Forest Loamy Wet Plains This ecological site occurs in close proximity to F220XY432AK on glacial till plains, however F220XY435AK occurs on poorly-drained soils with a high water table, resulting in unfavorable growing conditions. |
---|---|
R220XY436AK |
Maritime Graminoid Loamy Wet Plain This ecological site occurs in close proximity to F220XY432AK on glacial valley floors. The water table on site R220XY436AK occurs within 4 inches of the surface throughout the growing season resulting in ponded conditions and is dominated by sedges. |
Similar sites
F220XY427AK |
Maritime Forest Gravelly High Floodplain Ecological site F220XY427AK also supports a Sitka spruce forest, but is subject to a flood regime associated with active flood plains. |
---|---|
W1220X433 |
Maritime Forest Loamy Slopes Ecological sites F220XY433AK occurs on mountain slopes. |
F220XY435AK |
Maritime Forest Loamy Wet Plains Ecological site F220XY435AK supports a similar plant community, but occurs on wetter soils and exhibits lower levels of biomass production. |
F220XY460AK |
Maritime Forest Gravelly Alluvial Plains Ecological site F220XY460AK also supports a closed Sitka spruce forest that is controlled by windthrow events, but occurs on alluvial plains and terraces. |
F220XY466AK |
Maritime Forest Sandy Plains Eolian Ecological site F220XY466AK supports a closed Sitka spruce forest but soils are of eolian origin. |
F220XY468AK |
Maritime Forest Loamy Slopes Warm Ecological site F220XY468AK supports a similar plant community but occurs on steep slopes with paralithic contact around 20-40 inches. |
Table 1. Dominant plant species
Tree |
(1) Picea sitchensis |
---|---|
Shrub |
(1) Vaccinium |
Herbaceous |
(1) Listera cordata |
Physiographic features
This site occurs on outwash plains, outwash deltas, and glacial valley floors. Flooding is very rare and ponding does not occur. The water table occurs at more than 20 inches year-round and soil textures are sandy to loamy-skeletal. Slopes commonly range from 0-15% but can reach upwards of 45%. Elevation typically ranges from sea level to 325 feet.
Table 2. Representative physiographic features
Landforms |
(1)
Outwash plain
> Outwash plain
(2) Mountain valleys or canyons > Glacial-valley floor (3) Outwash plain > Outwash delta |
---|---|
Runoff class | Medium |
Flooding frequency | Very rare |
Ponding frequency | None |
Elevation | 325 ft |
Slope | 15% |
Water table depth | 20 in |
Aspect | W, NW, N, NE, E, SE, S, SW |
Table 3. Representative physiographic features (actual ranges)
Runoff class | Medium |
---|---|
Flooding frequency | None to very rare |
Ponding frequency | None |
Elevation | 330 ft |
Slope | 45% |
Water table depth | 20 in |
Climatic features
Cloudy skies, moderate temperatures, and abundant rainfall characterize the temperate maritime climate of this site. Frequent winter storms may consist of snow or heavy rainfall. Moderate to strong winds from the south and southeast are common before and during storms throughout the year. Annual precipitation ranges from 44-94 inches, and annual snowfall ranges from 30-70 inches along the coast and up to 200 inches at higher elevations (USDA 2006). The average annual temperature at lower elevations ranges from about 38-43 degrees F (3-6 degrees C). The frost-free period ranges from about 90-140 days, and the freeze-free period ranges from about 125-180 days.
Table 4. Representative climatic features
Frost-free period (characteristic range) | 89-139 days |
---|---|
Freeze-free period (characteristic range) | 126-181 days |
Precipitation total (characteristic range) | 44-94 in |
Frost-free period (actual range) | 77-147 days |
Freeze-free period (actual range) | 116-184 days |
Precipitation total (actual range) | 31-140 in |
Frost-free period (average) | 110 days |
Freeze-free period (average) | 153 days |
Precipitation total (average) | 74 in |
Figure 1. Monthly precipitation range
Figure 2. Monthly minimum temperature range
Figure 3. Monthly maximum temperature range
Figure 4. Monthly average minimum and maximum temperature
Figure 5. Annual precipitation pattern
Figure 6. Annual average temperature pattern
Climate stations used
-
(1) GUSTAVUS [USW00025322], Gustavus, AK
-
(2) GLACIER BAY [USC00503294], Gustavus, AK
-
(3) YAKUTAT STATE AP [USW00025339], Yakutat, AK
-
(4) SKAGWAY AP [USW00025335], Skagway, AK
-
(5) HAINES AP [USW00025323], Haines, AK
-
(6) SELDOVIA AP [USW00025516], Homer, AK
-
(7) MAIN BAY [USC00505604], Valdez, AK
-
(8) CORDOVA M K SMITH AP [USW00026410], Cordova, AK
-
(9) SITKA AIRPORT [USW00025333], Sitka, AK
-
(10) JUNEAU INTL AP [USW00025309], Juneau, AK
-
(11) ANNETTE ISLAND AP [USW00025308], Metlakatla, AK
-
(12) PETERSBURG 1 [USW00025329], Petersburg, AK
-
(13) KETCHIKAN INTL AP [USW00025325], Ketchikan, AK
-
(14) PELICAN [USC00507141], Hoonah, AK
Influencing water features
This site occurs on outwash plains and deltas where flooding is very rare. Most of the plant-available soil moisture enters the system as precipitation.
Soil features
Soils are formed in very deep glacial outwash and gravelly till occurring on glacial-outwash coastal plains directly adjacent to mountainous terrain. Soil textures are sandy to coarse-loamy or loamy-skeletal. The soil moisture regime is udic to aquic udic. Flooding very rarely occurs and ponding is not known to occur on these well drained soils.

Figure 7. Typical soil profile associated with Fossil soils in Glacier Bay National Park and Preserve-Gustavus Area, Alaska.

Figure 8. Typical soil profile associated with Geikie soils in Glacier Bay National Park and Preserve-Gustavus Area, Alaska.

Figure 9. Typical soil profile associated with Gustavus soils in Glacier Bay National Park and Preserve-Gustavus Area, Alaska.

Figure 10. Typical soil profile associated with Ibach soils in Glacier Bay National Park and Preserve-Gustavus Area, Alaska.

Figure 11. Typical soil profile associated with Tyeen soils in Glacier Bay National Park and Preserve-Gustavus Area, Alaska.

Figure 12. Typical soil profile associated with Scidmore soils in Glacier Bay National Park and Preserve-Gustavus Area, Alaska.
Table 5. Representative soil features
Parent material |
(1)
Outwash
(2) Till |
---|---|
Surface texture |
(1) Fine sandy loam (2) Medium gravelly coarse sand (3) Gravelly sandy clay (4) Very gravelly sandy loam |
Family particle size |
(1) Sandy (2) Loamy-skeletal |
Drainage class | Well drained |
Permeability class | Moderate to moderately rapid |
Depth to restrictive layer | 60 in |
Soil depth | 60 in |
Surface fragment cover <=3" | Not specified |
Surface fragment cover >3" | Not specified |
Available water capacity (0-10in) |
0.2 – 0.5 in |
Calcium carbonate equivalent (0-40in) |
Not specified |
Clay content (0-20in) |
1 – 15% |
Electrical conductivity (0-40in) |
Not specified |
Sodium adsorption ratio (0-40in) |
Not specified |
Soil reaction (1:1 water) (0-40in) |
3.8 – 8.7 |
Subsurface fragment volume <=3" (0-60in) |
31 – 69% |
Subsurface fragment volume >3" (0-60in) |
17% |
Table 6. Representative soil features (actual values)
Drainage class | Moderately well drained to well drained |
---|---|
Permeability class | Moderate to moderately rapid |
Depth to restrictive layer | 39 – 60 in |
Soil depth | 60 in |
Surface fragment cover <=3" | 27% |
Surface fragment cover >3" | 5% |
Available water capacity (0-10in) |
0.1 – 1.6 in |
Calcium carbonate equivalent (0-40in) |
5% |
Clay content (0-20in) |
1 – 15% |
Electrical conductivity (0-40in) |
Not specified |
Sodium adsorption ratio (0-40in) |
Not specified |
Soil reaction (1:1 water) (0-40in) |
3.7 – 8.7 |
Subsurface fragment volume <=3" (0-60in) |
69% |
Subsurface fragment volume >3" (0-60in) |
28% |
Ecological dynamics
During the past 250 years of glacial retreat, meltwater transported and deposited a large amount of silt and sediment via numerous short, high-gradient rivers. Alluvial and colluvial fans and long footslopes are common in the valleys along the base of the mountains. Drainageways dissect these fans and flats, which ultimately feed into the streams, rivers, and estuaries along the coastal plain.
The reference plant community phase for ecological site F220XY432AK is characterized as open needleleaf spruce forest. It is composed primarily of mature Sitka spruce and western hemlock with an extensive feathermoss understory. Common understory species include Sitka alder, oval-leaf blueberry, strawberryleaf raspberry, sidebells wintergreen, heartleaf twayblade, western rattlesnake plantain, stairstep moss, Schreber’s big red stem moss, and goose neck moss. Windthrow is common in certain areas throughout Glacier Bay. High wind events create naturally occurring gaps in the canopy by uprooting or snapping off mature trees. Windthrow facilitates a community phase transition from community phase 1.1 to community phase 1.3 or 1.4.
State and transition model

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Ecosystem states
State 1 submodel, plant communities
1.1a | - | Windthrow |
---|---|---|
1.2a | - | Natural succession |
1.3b | - | Windthrow recovery |
1.3a | - | Windthrow |
1.4a | - | Natural succession |
1.5a | - | Primary succession |
State 1
Reference State

The reference state supports five community phases, in which the reference community phase is represented by an open needleleaf forest. The presence of these and related communities are dictated temporally and spatially by the amount of time passed since the outwash plains were subject to glaciation and windthrow. All community phases in this report are characterized using the Alaska Vegetation Classification System (Viereck et al. 1992).
Resilience management. This state has been observed to be resilient and/or resistant to current disturbance drivers, lacking alternative states and at-risk communities.
Dominant plant species
-
Sitka spruce (Picea sitchensis), tree
-
western hemlock (Tsuga heterophylla), tree
-
oval-leaf blueberry (Vaccinium ovalifolium), shrub
-
splendid feather moss (Hylocomium splendens), other herbaceous
-
Schreber's big red stem moss (Pleurozium schreberi), other herbaceous
Community 1.1
Sitka spruce-western hemlock/oval-leaf blueberry-Alaska blueberry/splendid feather moss-Schreber’s big red stem moss

Figure 13. Typical plant community associated with community 1.1
The reference plant community phase is characterized as open needleleaf spruce forest (Viereck et al. 1992). It is composed primarily of mature Sitka spruce and western hemlock with extensive feathermoss coverage. Common understory species include Sitka alder, oval-leaf blueberry, Alaska blueberry, strawberryleaf raspberry, sidebells wintergreen, heartleaf twayblade, western rattlesnake plantain, splendid feather moss, Schreber’s big red stem, and goose neck moss. The vegetative stratum that characterized this community phase are tall trees, medium shrubs, and medium forb.
Dominant plant species
-
Sitka spruce (Picea sitchensis), tree
-
western hemlock (Tsuga heterophylla), tree
-
oval-leaf blueberry (Vaccinium ovalifolium), shrub
-
Alaska blueberry (Vaccinium alaskaense), shrub
-
heartleaf twayblade (Listera cordata), other herbaceous
-
splendid feather moss (Hylocomium splendens), other herbaceous
Table 7. Soil surface cover
Tree basal cover | 0-80% |
---|---|
Shrub/vine/liana basal cover | 0-77% |
Grass/grasslike basal cover | 0-1% |
Forb basal cover | 0-50% |
Non-vascular plants | 10-100% |
Biological crusts | 0-100% |
Litter | 5-30% |
Surface fragments >0.25" and <=3" | 0% |
Surface fragments >3" | 0% |
Bedrock | 0% |
Water | 0% |
Bare ground | 0% |
Community 1.2
Sitka spruce / oval-leaf blueberry - devil’s club / heartleaf twayblade-spreading woodfern

Figure 14. Typical plant community associated with community 1.2.
Community 1.2 is characterized by an open needleleaf forest (Viereck et al. 1992) that is primarily composed of mature Sitka spruce. Balsam poplar and western hemlock are present but in low densities. In this phase, balsam poplar is fading out due to stem exclusion while western hemlock is slowly establishing codominance with Sitka spruce. Common understory species include Sitka alder, oval-leaf blueberry, devil’s club, heartleaf twayblade, and spreading woodfern. The vegetative stratum that characterized this community phase is tall trees, medium shrubs, and medium forbs. The ground cover consists of feathermoss species, large downed woody debris, and litter. Common feathermoss species include stairstep moss and Schreber’s big red stem.
Dominant plant species
-
Sitka spruce (Picea sitchensis), tree
-
oval-leaf blueberry (Vaccinium ovalifolium), shrub
-
devilsclub (Oplopanax horridus), shrub
Table 8. Soil surface cover
Tree basal cover | 0-85% |
---|---|
Shrub/vine/liana basal cover | 0-80% |
Grass/grasslike basal cover | 0-1% |
Forb basal cover | 0-50% |
Non-vascular plants | 10-100% |
Biological crusts | 0% |
Litter | 5-75% |
Surface fragments >0.25" and <=3" | 0% |
Surface fragments >3" | 0% |
Bedrock | 0% |
Water | 0% |
Bare ground | 0% |
Community 1.3
Balsam poplar-Sitka spruce/Sitka alder-Sitka willow/common ladyfern-spreading woodfern

Figure 15. Typical plant community associated with community 1.3
Community phase 1.3 is characterized by an open mixed forest with balsam poplar the most common overstory species. Sitka spruce is common, but generally as young, regenerating trees. Common understory species include Sitka alder, Sitka willow, salmonberry, devil’s club, common ladyfern, and spreading woodfern. The vegetative stratum that characterizes this community phase is medium trees, medium shrubs, and medium forbs. The ground cover is largely herbaceous litter with low coverages of feathermoss.
Dominant plant species
-
balsam poplar (Populus balsamifera), tree
-
Sitka alder (Alnus viridis ssp. sinuata), shrub
-
Sitka willow (Salix sitchensis), shrub
-
splendid feather moss (Hylocomium splendens), other herbaceous
-
Schreber's big red stem moss (Pleurozium schreberi), other herbaceous
Table 9. Soil surface cover
Tree basal cover | 0-65% |
---|---|
Shrub/vine/liana basal cover | 32-90% |
Grass/grasslike basal cover | 0-2% |
Forb basal cover | 10-38% |
Non-vascular plants | 0-90% |
Biological crusts | 0% |
Litter | 15-95% |
Surface fragments >0.25" and <=3" | 0% |
Surface fragments >3" | 0% |
Bedrock | 0% |
Water | 0% |
Bare ground | 0% |
Community 1.4
Sitka alder-Sitka willow/common ladyfern-spreading woodfern

Community phase 1.4 is characterized as closed tall scrub (Viereck et al. 1992). It consists of a canopy of dense shrubs with a mosaic of forb species and significant litter coverage. Common species include Sitka alder, Sitka willow, salmonberry, Barclay’s willow, common ladyfern, and spreading woodfern. The vegetative stratum that characterizes this community is tall shrub and medium forb. The ground cover is largely herbaceous litter with some feathermoss species.
Dominant plant species
-
Sitka alder (Alnus viridis ssp. sinuata), shrub
-
Sitka willow (Salix sitchensis), shrub
-
spreading woodfern (Dryopteris expansa), other herbaceous
-
common ladyfern (Athyrium filix-femina), other herbaceous
Table 10. Soil surface cover
Tree basal cover | 0-40% |
---|---|
Shrub/vine/liana basal cover | 0-100% |
Grass/grasslike basal cover | 0-15% |
Forb basal cover | 0-2% |
Non-vascular plants | 0-60% |
Biological crusts | 0% |
Litter | 45-85% |
Surface fragments >0.25" and <=3" | 0-10% |
Surface fragments >3" | 0% |
Bedrock | 0% |
Water | 0% |
Bare ground | 0% |
Community 1.5
Drummond’s mountain-avens–Sitka willow / Ceratodon moss

Figure 16. Typical plant community associated with community 1.5
Community 1.5 is in the pioneering stage following deglaciation and is characterized as Dryas dwarf scrub (Viereck et al. 1992). Drummond’s mountain-avens is most common. Other species include Sitka willow, Sitka alder, western pearly everlasting, and alpine milkvetch. The vegetative stratum for this community phase is low shrubs. The ground cover is rock and litter. Some areas are bare.
Dominant plant species
-
Drummond's mountain-avens (Dryas drummondii), shrub
-
Sitka willow (Salix sitchensis), shrub
-
ceratodon moss (Ceratodon purpureus), other herbaceous
Table 11. Soil surface cover
Tree basal cover | 0-10% |
---|---|
Shrub/vine/liana basal cover | 0-60% |
Grass/grasslike basal cover | 0% |
Forb basal cover | 0-25% |
Non-vascular plants | 1-75% |
Biological crusts | 0% |
Litter | 5-50% |
Surface fragments >0.25" and <=3" | 0-75% |
Surface fragments >3" | 0% |
Bedrock | 0% |
Water | 0% |
Bare ground | 0-10% |
Pathway 1.1a
Community 1.1 to 1.3


Windthrow event damages or removes overstory species.
Pathway 1.2a
Community 1.2 to 1.1


Succession following glacial retreat or windthrow event
Pathway 1.3b
Community 1.3 to 1.2


Windthrow recovery. Sitka spruce regenerates and becomes a dominant component of the overstory community.
Pathway 1.3a
Community 1.3 to 1.4


Windthrow event damages or removes overstory species.
Pathway 1.4a
Community 1.4 to 1.3


Natural succession following glacial retreat or windthrow event
Pathway 1.5a
Community 1.5 to 1.4


Primary succession following glacial retreat
Additional community tables
Table 12. Community 1.1 forest overstory composition
Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | Diameter (in) | Basal area (square ft/acre) |
---|---|---|---|---|---|---|---|
Table 13. Community 1.1 forest understory composition
Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | |
---|---|---|---|---|---|---|
Grass/grass-like (Graminoids)
|
||||||
Piper's woodrush | LUPI2 | Luzula piperi | – | – | 0–1 | |
bluegrass | POA | Poa | – | – | 0–1 | |
longawn sedge | CAMA11 | Carex macrochaeta | – | – | 0–1 | |
sedge | CAREX | Carex | – | – | 0–1 | |
bluebell bellflower | CARO2 | Campanula rotundifolia | – | – | 0–1 | |
tufted hairgrass | DECE | Deschampsia cespitosa | – | – | 0–1 | |
Forb/Herb
|
||||||
western rattlesnake plantain | GOOB2 | Goodyera oblongifolia | – | – | 0–35 | |
false lily of the valley | MADI | Maianthemum dilatatum | – | – | 0–20 | |
heartleaf twayblade | LICO6 | Listera cordata | – | – | 0–20 | |
single delight | MOUN2 | Moneses uniflora | – | – | 0–10 | |
sidebells wintergreen | ORSE | Orthilia secunda | – | – | 0–10 | |
twistedstalk | STREP3 | Streptopus | – | – | 0–10 | |
liverleaf wintergreen | PYAS | Pyrola asarifolia | – | – | 0–5 | |
stiff clubmoss | LYAN2 | Lycopodium annotinum | – | – | 0–5 | |
field horsetail | EQAR | Equisetum arvense | – | – | 0–5 | |
horsetail | EQUIS | Equisetum | – | – | 0–5 | |
fernleaf goldthread | COAS | Coptis aspleniifolia | – | – | 0–5 | |
northwestern twayblade | LICA10 | Listera caurina | – | – | 0–2 | |
claspleaf twistedstalk | STAM2 | Streptopus amplexifolius | – | – | 0–2 | |
threeleaf foamflower | TITR | Tiarella trifoliata | – | – | 0–2 | |
small twistedstalk | STST3 | Streptopus streptopoides | – | – | 0–1 | |
foamflower | TIARE | Tiarella | – | – | 0–1 | |
Canadian burnet | SACA14 | Sanguisorba canadensis | – | – | 0–1 | |
wintergreen | PYROL | Pyrola | – | – | 0–1 | |
western rattlesnakeroot | PRAL | Prenanthes alata | – | – | 0–1 | |
American skunkcabbage | LYAM3 | Lysichiton americanus | – | – | 0–1 | |
clubmoss | LYCOP2 | Lycopodium | – | – | 0–1 | |
Scottish licorice-root | LISC3 | Ligusticum scoticum | – | – | 0–1 | |
sweetcicely | OSBE | Osmorhiza berteroi | – | – | 0–1 | |
sweetroot | OSMOR | Osmorhiza | – | – | 0–1 | |
pinesap | MOHY3 | Monotropa hypopitys | – | – | 0–1 | |
threeleaf goldthread | COTR2 | Coptis trifolia | – | – | 0–1 | |
northern groundcone | BORO | Boschniakia rossica | – | – | 0–1 | |
fireweed | CHAN9 | Chamerion angustifolium | – | – | 0–1 | |
bride's feathers | ARDI8 | Aruncus dioicus | – | – | 0–1 | |
variegated scouringrush | EQVA | Equisetum variegatum | – | – | 0–1 | |
beach strawberry | FRCH | Fragaria chiloensis | – | – | 0–1 | |
water horsetail | EQFL | Equisetum fluviatile | – | – | 0–1 | |
common cowparsnip | HEMA80 | Heracleum maximum | – | – | 0–1 | |
fringed willowherb | EPCI | Epilobium ciliatum | – | – | 0–1 | |
saxifrage | SAXIF | Saxifraga | – | – | – | |
Fern/fern ally
|
||||||
western oakfern | GYDR | Gymnocarpium dryopteris | – | – | 0–6 | |
spreading woodfern | DREX2 | Dryopteris expansa | – | – | 0–6 | |
common ladyfern | ATFI | Athyrium filix-femina | – | – | 0–5 | |
ladyfern | ATHYR | Athyrium | – | – | 0–1 | |
deer fern | BLSP | Blechnum spicant | – | – | 0–1 | |
brittle bladderfern | CYFR2 | Cystopteris fragilis | – | – | 0–1 | |
northern hollyfern | POLO4 | Polystichum lonchitis | – | – | 0–1 | |
Shrub/Subshrub
|
||||||
oval-leaf blueberry | VAOV | Vaccinium ovalifolium | – | – | 0–70 | |
devilsclub | OPHO | Oplopanax horridus | – | – | 0–30 | |
strawberryleaf raspberry | RUPE | Rubus pedatus | – | – | 0–25 | |
salmonberry | RUSP | Rubus spectabilis | – | – | 0–20 | |
Sitka alder | ALVIS | Alnus viridis ssp. sinuata | – | – | 0–20 | |
bunchberry dogwood | COCA13 | Cornus canadensis | – | – | 0–20 | |
green alder | ALVI5 | Alnus viridis | – | – | 0–17 | |
blueberry | VACCI | Vaccinium | – | – | 0–15 | |
red huckleberry | VAPA | Vaccinium parvifolium | – | – | 0–10 | |
pipsissewa | CHUM | Chimaphila umbellata | – | – | 0–5 | |
rusty menziesia | MEFE | Menziesia ferruginea | – | – | 0–5 | |
Aleutian mountainheath | PHAL4 | Phyllodoce aleutica | – | – | 0–1 | |
stink currant | RIBR | Ribes bracteosum | – | – | 0–1 | |
prickly currant | RILA | Ribes lacustre | – | – | 0–1 | |
trailing black currant | RILA3 | Ribes laxiflorum | – | – | 0–1 | |
blackberry | RUBUS | Rubus | – | – | 0–1 | |
willow | SALIX | Salix | – | – | 0–1 | |
red elderberry | SARA2 | Sambucus racemosa | – | – | 0–1 | |
Lapland cornel | COSU4 | Cornus suecica | – | – | 0–1 | |
squashberry | VIED | Viburnum edule | – | – | 0–1 | |
red baneberry | ACRU2 | Actaea rubra | – | – | 0–1 | |
dwarf mistletoe | ARCEU | Arceuthobium | – | – | 0–1 | |
dwarf bilberry | VACE | Vaccinium cespitosum | – | – | – | |
Sitka willow | SASI2 | Salix sitchensis | – | – | – | |
russet buffaloberry | SHCA | Shepherdia canadensis | – | – | – | |
western mountain ash | SOSI2 | Sorbus sitchensis | – | – | – | |
Tree
|
||||||
western hemlock | TSHE | Tsuga heterophylla | – | – | 2–80 | |
mountain hemlock | TSME | Tsuga mertensiana | – | – | 0–31 | |
balsam poplar | POBA2 | Populus balsamifera | – | – | 0–5 | |
Nonvascular
|
||||||
splendid feather moss | HYSP70 | Hylocomium splendens | – | – | 0–90 | |
Schreber's big red stem moss | PLSC70 | Pleurozium schreberi | – | – | 0–80 | |
goose neck moss | RHYTI2 | Rhytidiadelphus | – | – | 0–60 | |
rhizomnium moss | RHGL70 | Rhizomnium glabrescens | – | – | 0–30 | |
goose neck moss | RHLO70 | Rhytidiadelphus loreus | – | – | 0–25 | |
rough goose neck moss | RHTR70 | Rhytidiadelphus triquetrus | – | – | 0–20 | |
knights plume moss | PTCR70 | Ptilium crista-castrensis | – | – | 0–20 | |
dicranum moss | DICRA8 | Dicranum | – | – | 0–20 | |
tree climacium moss | CLDE70 | Climacium dendroides | – | – | 0–10 | |
rhizomnium moss | RHIZO2 | Rhizomnium | – | – | 0–10 | |
rhytidium moss | RHYTI4 | Rhytidium | – | – | 0–10 | |
beard lichen | USNEA2 | Usnea | – | – | 0–10 | |
polytrichum moss | POLYT5 | Polytrichum | – | – | 0–10 | |
claopodium moss | CLAOP | Claopodium | – | – | 0–6 | |
claopodium moss | CLCR4 | Claopodium crispifolium | – | – | 0–5 | |
hookeria moss | HOLU | Hookeria lucens | – | – | 0–5 | |
tube lichen | HYEN60 | Hypogymnia enteromorpha | – | – | 0–5 | |
tube lichen | HYPOG2 | Hypogymnia | – | – | 0–5 | |
felt lichen | PELTI2 | Peltigera | – | – | 0–5 | |
sphagnum | SPHAG2 | Sphagnum | – | – | 0–5 | |
racomitrium moss | RACOM | Racomitrium | – | – | 0–5 | |
dicranum moss | DISC71 | Dicranum scoparium | – | – | 0–3 | |
hypnum moss | HYPNU2 | Hypnum | – | – | 0–2 | |
lung lichen | LOBAR2 | Lobaria | – | – | 0–2 | |
lung lichen | LOLI60 | Lobaria linita | – | – | 0–1 | |
lung lichen | LOPU60 | Lobaria pulmonaria | – | – | 0–1 | |
peppermint drop lichen | ICER | Icmadophila ericetorum | – | – | 0–1 | |
peppermint drop lichen | ICMAD | Icmadophila | – | – | 0–1 | |
isothecium moss | ISOTH | Isothecium | – | – | 0–1 | |
undulate plagiothecium moss | PLUN4 | Plagiothecium undulatum | – | – | 0–1 | |
bullseye lichen | PLACO | Placopsis | – | – | 0–1 | |
kidney lichen | NEPHR3 | Nephroma | – | – | 0–1 | |
felt lichen | PEAP60 | Peltigera aphthosa | – | – | 0–1 | |
hookeria moss | HOOKE | Hookeria | – | – | 0–1 | |
cup lichen | CLSC60 | Cladonia scabriuscula | – | – | 0–1 | |
cup lichen | CLSQ60 | Cladonia squamosa | – | – | 0–1 | |
reindeer lichen | CLADI3 | Cladina | – | – | 0–1 | |
cup lichen | CLADO3 | Cladonia | – | – | 0–1 | |
horsehair lichen | BRYOR2 | Bryoria | – | – | 0–1 |
Table 14. Community 1.2 forest overstory composition
Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | Diameter (in) | Basal area (square ft/acre) |
---|---|---|---|---|---|---|---|
Table 15. Community 1.2 forest understory composition
Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | |
---|---|---|---|---|---|---|
Table 16. Community 1.3 forest overstory composition
Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | Diameter (in) | Basal area (square ft/acre) |
---|---|---|---|---|---|---|---|
Table 17. Community 1.3 forest understory composition
Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | |
---|---|---|---|---|---|---|
Table 18. Community 1.4 forest overstory composition
Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | Diameter (in) | Basal area (square ft/acre) |
---|---|---|---|---|---|---|---|
Table 19. Community 1.4 forest understory composition
Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | |
---|---|---|---|---|---|---|
Table 20. Community 1.5 forest overstory composition
Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | Diameter (in) | Basal area (square ft/acre) |
---|---|---|---|---|---|---|---|
Table 21. Community 1.5 forest understory composition
Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | |
---|---|---|---|---|---|---|
Interpretations
Supporting information
Inventory data references
NASIS ID Plant community
13NP00304 Community 1.1
13NP00602 Community 1.1
13TD00904 Community 1.1
13NP00101 Community 1.1
13NP00102 Community 1.1
13NP01401 Community 1.1
13NP05702 Community 1.1
2015AK105124 Community 1.1
2015AK105125 Community 1.1
14DM01101 Community 1.1
14JP02301 Community 1.1
14JP02401 Community 1.1
14JP02404 Community 1.1
14JP02503 Community 1.1
14NP02202 Community 1.1
14NP02203 Community 1.1
14NP02702 Community 1.1
14NP02703 Community 1.1
2015AK105101 Community 1.1
2015AK105103 Community 1.1
2015AK105109 Community 1.1
2015AK105119 Community 1.1
2015AK105120 Community 1.1
2015AK105121 Community 1.1
14DM01202 Community 1.1
14NP02201 Community 1.1
14DM01701 Community 1.1
14JP02102 Community 1.1
13NP01403 Community 1.1
13NP05201 Community 1.1
13NP05701 Community 1.1
13NP05703 Community 1.1
13TD01501 Community 1.1
13TD01503 Community 1.1
14NP00901 Community 1.1
14NP01702 Community 1.1
14NP01704 Community 1.1
2015AK105003 Community 1.1
13TD01601 Community 1.2
13TD01603 Community 1.2
14NP01701 Community 1.2
14DM01301 Community 1.2
13DM01204 Community 1.2
13DM02104 Community 1.2
13NP01501 Community 1.2
13NP03701 Community 1.2
13NP03702 Community 1.2
14JP02402 Community 1.2
14NP02704 Community 1.2
2015AK105102 Community 1.2
2015AK105104 Community 1.2
2015AK105110 Community 1.2
2015AK105118 Community 1.2
14DM01204 Community 1.2
14JP02104 Community 1.2
13NP02301 Community 1.2
13NP03101 Community 1.2
13NP03102 Community 1.2
13NP05202 Community 1.2
13TD01502 Community 1.2
13TD06901 Community 1.2
13NP01201 community 1.3
14DM01801 community 1.3
14DM01302 community 1.3
14JP02403 community 1.3
14NP02701 community 1.3
13NP01605 community 1.3
13NP02302 community 1.3
13TD01301 community 1.3
13TD02001 community 1.3
13TD02403 community 1.3
13TD02702 community 1.3
13TD02703 community 1.3
13TD02704 community 1.3
13NP02401 Community 1.4
13NP02405 Community 1.4
13NP02802 Community 1.4
13NP02803 Community 1.4
13NP03104 Community 1.4
13NP04101 Community 1.4
13NP05301 Community 1.4
13NP05303 Community 1.4
13NP05304 Community 1.4
13TD01101 Community 1.4
13TD01801 Community 1.4
13TD01802 Community 1.4
13TD02101 Community 1.4
13TD02102 Community 1.4
13TD02103 Community 1.4
13TD03405 Community 1.4
13TD06803 Community 1.4
14DM01802 Community 1.4
13NP01601 Community 1.4
13NP01602 Community 1.4
13NP02801 Community 1.4
13NP05302 Community 1.4
13TD01504 Community 1.4
13TD02402 Community 1.4
13TD02601 Community 1.4
13TD06101 Community 1.4
13TD06501 Community 1.4
13NP01603 community 1.5
13NP01803 community 1.5
13NP04201 community 1.5
Other references
Brokaw, N.V.L. 1985b. Gap-phase regeneration in a tropical forest. Ecology 66: 682-687.
Chapin, F.S., L.R. Walker, C.L. Fastie, and L.C. Sharman. 1994. Mechanisms of primary succession following deglaciation at Glacier Bay, Alaska. Ecological Monographs 64: 149-175.
Hall, D.K., C.S. Benton, and W.O. Field, 1994. Changes of glaciers in Glacier Bay, Alaska, using ground and satellite measurements. Physical Geography 16(1): 27-41.
Hall, M.H.P., and D. Fagre. 2003. Modeled climate-induced glacier change in Glacier National Park 1850–2100. BioScience 53:131-140.
Lawson, D.E. 2015. An overview of selected glaciers in Glacier Bay. National Park Service. Retrieved August 15, 2010.
Reiners, W.A., I.A. Worley, and D.B. Lawrence. 1971. Plant diversity in a chronosequence at Glacier Bay, Alaska. Ecology 52: 55-69.
Schoeneberger, P.J., and D.A. Wysocki. 2012. Geomorphic Description System, Version 4.2. Natural Resources Conservation Service, National Soil Survey Center, Lincoln, Nebraska.
Schoeneberger, P.J., D.A. Wysocki, E.C. Benham, and W.D. Broderson, editors. 2012. Field book for describing and sampling soils. Version 3.0. U.S. Department of Agriculture, Natural Resources Conservation Service.
Soil Survey Division Staff. 2017. Soil survey manual. U.S. Department of Agriculture Handbook 18.
Viereck, L.A., C.T. Dyrness, A.R. Batten, and K.J. Wezlick. 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.
Contributors
Tyler Annetts
Jamin Johanson
Blaine Spellman
Phil Barber
Approval
Marji Patz, 3/10/2025
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 | 03/11/2025 |
Approved by | Marji Patz |
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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The Ecosystem Dynamics Interpretive Tool is an information system framework developed by the USDA-ARS Jornada Experimental Range, USDA Natural Resources Conservation Service, and New Mexico State University.
Click on box and path labels to scroll to the respective text.
Ecosystem states
State 1 submodel, plant communities
1.1a | - | Windthrow |
---|---|---|
1.2a | - | Natural succession |
1.3b | - | Windthrow recovery |
1.3a | - | Windthrow |
1.4a | - | Natural succession |
1.5a | - | Primary succession |