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Ecological site AX003X05X003

Western Cascades Mesic Udic Forest Group

Last updated: 2/29/2024
Accessed: 05/09/2024

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General information

Provisional. A provisional ecological site description has undergone quality control and quality assurance review. It contains a working state and transition model and enough information to identify the ecological site.

MLRA notes

Major Land Resource Area (MLRA): 003X–Olympic and Cascade Mountains

The Cascade and Olympic Mountains (MLRA 3) include the west slope and parts of the east slope of the Cascades Mountains in Washington and Oregon. The Olympic Mountains in Washington State are also included. These mountains are part of a volcanic arc located at a convergent plate boundary. Volcanic rocks predominate but metamorphic and sedimentary rocks occur in the North Cascades and Olympic Mountains. Topography is generally dissected and steep, but some areas consist of constructional volcanic platforms and isolated stratovolcanoes. Elevation is usually 500 to 6000 feet but reaches to 14,410 ft at the summit of Mount Rainier. Many areas hosted alpine glaciers or ice sheets during the Pleistocene, and a few remain today.
Climate becomes cooler and more moist with increasing elevation and latitude. Low elevations experience a long growing season and mild temperatures. High elevations can accumulate snowpack lasting into summer and frost may occur in any month. Average annual precipitation ranges from 60 to 180 inches in most areas. Most precipitation falls during the fall, winter, and spring during low-intensity frontal storms. Summers are relatively dry. Average annual temperature is 27 to 50 degrees F. The frost-free period is 10 to 180 days.

LRU notes

The Western Cascades land resource unit (LRU E) is located in western Oregon. It is bounded by the Santiam River on the north, the High Cascade volcanic platform on the east, the Rogue-Umpqua Divide on the south, and the Willamette and Umpqua Valleys on the west. This area is equivalent to the area generally known as the “Old Cascades.”
Bedrock consists of basalt and andesite of the Sardine Formation overlying the Little Butte Volcanic Series which contains soft tuff (Orr, et al. 1992). The Sardine Formation “cap” is absent at many locations. Topography is dissected and steep in most areas. Areas of low relief contain ancient and contemporary landslides. Alpine glaciation occurred in headwater basins during the Pleistocene but subsequent mass movement has partially obscured glacial features (Noller, et al. 2016).
Soil moisture regime is udic or aquic. Soil temperature regime ranges from mesic to cryic. Soils in this LRU generally have higher apparent clay content compared with those to the north and Spodosols do not occur. Most soils contain an appreciable amount of volcanic glass. Inceptisols usually have isotic mineralogy. Andisols are usually amorphic and meet the second criteria for andic soil properties (Soil Survey Staff, 2014). Ultisols can occur at the lowest elevations.
Conifer forest is the dominant vegetation. Natural fire is dominantly moderately frequent, mixed-severity (Spies, et al. 2018). Franklin and Spies (1991) noted an increase in tree bole fire scars south of 44.5 degrees latitude in the Oregon Cascades. This LRU hosts small amounts of fire-tolerant species common in the Siskiyou-Trinity Area (MLRA 5) but absent in areas to the north. These species include Pacific madrone (Arbutus menziesii), incense cedar (Calocedrus decurrens), giant chinkapin (Chrysolepis chrysophylla), and sugar pine (Pinus lambertiana).
At low to mid elevations, Douglas-fir (Pseudotsuga menziesii) is a long-lived, early-seral tree; western hemlock (Tsuga heterophylla) is an associated shade-tolerant tree. Red alder (Alnus rubra) is a short-lived, early-seral tree. It occurs ephemerally on uplands but persists on wet or repeatedly-disturbed sites.
At high elevations, Noble fir (Abies procera) is an early-seral tree; Pacific silver fir (Abies amabilis) is an associated shade-tolerant tree. Sitka alder (Alnus viridis ssp. sinuata) and vine maple (Acer circinatum) form persistent shrubfields on sites subject to heavy snowpack or avalanches. Wetlands typically support shrubby or herbaceous vegetation.

Classification relationships

This ecological site group description covers a variety of warm western hemlock plant associations including the following (McCain and Diaz 2002):

• Western hemlock / vine maple / western swordfern
• Western hemlock / vine maple - salal / western swordfern
• Western hemlock / sweet after death-DRY
• Western hemlock / salal
• Western hemlock / Cascade barberry
• Western hemlock / Cascade barberry - salal
• Western hemlock / Cascade barberry / Oregon oxalis
• Western hemlock / Cascade barberry / western swordfern
• Western hemlock / Oregon oxalis
• Western hemlock / swordfern

Ecological site concept

This forested site occurs in the warmer, sometimes drier, portion of the western hemlock zone. Soil temperature regime is mesic, and soil moisture regime is udic. Forest litter turnover and associated nutrient cycling can be rapid compared with cooler sites. Elevation is typically 1500 to 3000 feet.

Associated sites

AX003X05X004	Western Cascades Frigid Udic Forest Group Higher elevations on the Western Cascades, slightly cooler areas.

AX003X05X004

Western Cascades Frigid Udic Forest Group

Higher elevations on the Western Cascades, slightly cooler areas.

Similar sites

AX003X03X004	Glaciated Western Cascades Frigid Udic Forest Group Similar position, but on the Glaciated areas of the Western Cascades.

AX003X03X004

Glaciated Western Cascades Frigid Udic Forest Group

Similar position, but on the Glaciated areas of the Western Cascades.

Table 1. Dominant plant species

Tree	(1) Pseudotsuga menziesii (2) Tsuga heterophylla
Shrub	(1) Mahonia nervosa (2) Gaultheria shallon
Herbaceous	Not specified

Legacy ID

F003XE003OR

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Physiographic features

Landform: mountain slopes, landslides
Elevation: 1500 to 3000 feet
Slope: 0 to 90 percent
Aspect: all aspects
Flooding: none
Ponding: none

Table 2. Representative physiographic features

Landforms	(1) Mountain slope (2) Landslide
Flooding frequency	None
Ponding frequency	None
Elevation	1,500 – 3,000 ft
Slope	90%

Soil features

Drainage class: well drained or moderately well drained
Parent material: colluvium, residuum, till; mixed with volcanic ash
Restrictive feature(s): shallow to very deep to bedrock
Soil temperature regime: mesic
Soil moisture regime: udic
Soil reaction: moderately acid or strongly acid
Soil mineralogy: isotic

Soils are usually very deep and well drained, but those with a brief seasonal water table still capable of supporting Douglas-fir (Pseudotsuga menziesii) are included in this concept. The rooting zone is usually moist but may be dry up to 45 consecutive days in late summer. Litter layers under mature forest are usually thin, slightly decomposed, and lie above a dark-colored, granular topsoil. O horizons associated with this site on the Willamette National Forest were usually 3 to 5 cm thick (inner quartiles, n=139). Organic materials were predominantly slightly decomposed; only 18 percent of pedons contained moderately or highly decomposed plant materials (Rand, 2020). Millipedes (Harpaphe haydeniana) and non-anecic earthworms may be responsible for fragmenting and mixing litter into the A horizon (Moldenke, et al. 2000). Soils usually have umbric epipedons. Andic soil properties derived from the weathering of volcanic ash are usually present but limited to the upper part of the soil. Inceptisols and Ultisols are common soil orders. Apparent fine-earth textures are loams, silt loams, clay loams, or silty clay loams. Apparent clay content ranges from 18 to 35 percent.

Table 3. Representative soil features

Parent material	(1) Colluvium (2) Residuum (3) Till (4) Volcanic ash
Drainage class	Moderately well drained to well drained

Ecological dynamics

Central Concept: This forested site occurs in the warmer, sometimes drier, portion of the western hemlock zone. Soil temperature regime is mesic, and soil moisture regime is udic. Forest litter turnover and associated nutrient cycling can be rapid compared with cooler sites. Elevation is typically 1500 to 3000 feet.
Range in Variability: Duration of dryness linked to local landscape position, aspect, and soil depth may define subtypes with distinctive reference communities. Southern exposures and convex slopes may support drought-tolerant communities. Northern exposures and concave slopes may support moist communities. Soils with a seasonal water table may restrict rooting depth for some species.
Disturbance: Fire is the dominant natural landscape level driver. Mixed severity fires dominate in this vegetation type, with areas of low (< 30%), moderate (30-70%) and high (> 70%) overstory mortality expressed within fires. Historical fire frequency has varied from 50 to 200 years mean fire return intervals (MFRI) (Morrison and Swanson 1990, Tepley et al. 2013, Spies et al. 2018). Wind, insects and pathogens, and infrequent landslides may also shape forest composition and pattern at finer scales. Human management is prevalent in this type, with activities such as regeneration harvest and thinning occurring within its range and dominating phase trajectories over fire (Spies et al. 2013).
Vegetation composition: Douglas-fir (Pseudotsuga menziesii (Mirb.) Franco), western hemlock, western redcedar (Thuja plicata Donn ex D. Don), and bigleaf maple (Acer macrophyllum Pursh) are common tree associates that span most of these types. Pacific yew (Taxus brevifolia Nutt.) is scattered throughout. Other trees, such as Pacific dogwood (Cornus nuttallii Audubon ex Torr. & A. Gray) and giant chinquapin (Chrysolepis chrysophylla (Douglas ex Hook.) Hjelmqvist) are found more commonly in the warmer, and sometimes drier portions of this type (McCain and Diaz 2002).
Understory shrub species are varied. Low growing, evergreen shrubs such as Cascade barberry (Mahonia nervosa (Pursh) Nutt.) and salal (Gaultheria shallon Pursh) are common dominants and key indicators of this vegetation group. California hazelnut (Corylus cornuta Marshall var. californica (A. DC.) Sharp) and vine maple (Acer circinatum Pursh) are common tall shrubs. California blackberry (Rubus ursinus Cham. & Schltdl), dwarf rose (Rosa gymnocarpa Nutt.), and red huckleberry (Vaccinium parvifolium Sm.) are scattered throughout. On drier, warmer sites oceanspray (Holodiscus discolor (Pursh) Maxim.) and common whipplea (Whipplea modesta Torr.) can be found (McCain and Diaz 2002).
A diverse array of herbs occupies this these sites. Sweet after death (Achlys triphylla (Sm.) DC), American trailplant (Adenocaulon bicolor Hook.), Columbian windflower (Anemone deltoidea Hook.), drops-of-gold (Prosartes hookeri Torr. var. hookeri), western rattlesnake plantain (Goodyera oblongifolia Raf.), twinflower (Linnaea borealis L.), starry false lily of the valley (Maianthemum stellatum (L.) Link), western brackenfern (Pteridium aquilinum (L.) Kuhn), Pacific trillium (Trillium ovatum Pursh), white insideout flower (Vancouveria hexandra (Hook.) C. Morren & Decne.) and western swordfern (Polystichum munitum (Kaulf.) C. Presl) often occur together. On moister sites Oregon oxalis (Oxalis oregana Nutt.) becomes more dominant (McCain and Diaz 2002).
Structural Descriptions Used in State and Transition Model: Phases are described by size class, cover class and layering. Size class description refers to either the average diameter of the dominant and co-dominant trees (quadratic mean diameter or qmd) in the state and transition model or the general sizes by species in the following narrative.
Size Class
Grass Forb/Seedling Sapling Pole Small Medium Large/Giant
DBH (inches) NA 0.1-4.9 5-9.9 10-19.9 20-29.9 =30
Canopy Cover Class
Open Moderate Closed
Canopy cover (%) <10 10-60 >60

State and transition model

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

Ecosystem states

State 1 submodel, plant communities

1.1. Reference Community: Douglas-fir - western hemlock / evergreen shrubs / forbs

1.2. Douglas-fir / vine maple - evergreen shrubs - California blackberry / forbs

1.3. Douglas-fir / evergreen shrubs / forbs

1.4. Douglas-fir / evergreen shrubs / western swordfern - forbs

1.5. Douglas-fir - western hemlock / evergreen shrubs / forbs

Communities 1, 5 and 2 (additional pathways)

1.1. Reference Community: Douglas-fir - western hemlock / evergreen shrubs / forbs

1.5. Douglas-fir - western hemlock / evergreen shrubs / forbs

1.2. Douglas-fir / vine maple - evergreen shrubs - California blackberry / forbs

State 1

Community 1.1
Reference Community: Douglas-fir - western hemlock / evergreen shrubs / forbs

Dominant and co-dominant large and giant Douglas-fir, with large western hemlock are indicators of reference condition. Small to large western hemlock and Douglas-fir can be found in the mid canopy, depending on fire history and gap dynamics. Other trees, such as coniferous small to large western redcedar, and small to large hardwoods, such as bigleaf maple may be scattered throughout stands. Shade tolerant western hemlock, western redcedar and Pacific yew, as well as bigleaf maple can regenerate and survive under low light levels. Shade intolerant Douglas-fir may regenerate in large gaps, and after moderate severity fire (Tepley et al. 2013). A diverse understory is found in this condition. Evergreen shrubs, such as Cascade barberry and salal are found in moderate to high cover (averages ranging 25-60%) Vine maple, and to a lesser extent California hazelnut contribute to the tall shrub cover that averages 10-40%. A diverse mix of herbs, such as sweet after death, American trailplant, Columbian windflower, drops-of-gold, Oregon oxalis, western swordfern and western rattlesnake plantain can be found with cover averaging 15-50% (McCain and Diaz 2002). Growth from community phase 1.4 and 1.5 are the dominant pathways producing this condition. Moderate to low severity fire and background mortality (insects, pathogens, wind, etc.) processes also serve to maintain a heterogeneous horizontal and vertical range of compositional and live and dead structural conditions, with multi-layered forest intermixed with gaps of various sizes. Small to giant snags are present, as well as down wood (Mellen-McLean et al. 2017). CP1.1 Reference Community. Douglas-fir - western hemlock / evergreen shrubs / forbs Large/Giant, multi-layered, moderate-closed canopy, scattered diverse sized gaps, regenerating shade tolerant and intolerant tree species Age class: >100 years

Community 1.2
Douglas-fir / vine maple - evergreen shrubs - California blackberry / forbs

This community phase is a post-disturbance, early seral condition, resulting from high severity fire or regeneration harvest. Open canopy conditions, with or without legacy structure and tree regeneration characterize this phase. Douglas-fir may exist as scattered live legacy overstory. Post-fire conditions may consist of high densities of small to large/giant snags, resulting in diverse cover of down wood (Mellen-McLean et al. 2017). Seedlings of various coniferous species may be present, with Douglas-fir likely dominating. Bigleaf maple may persist through basal sprouting. Early seral trees, such as bitter cherry (Prunus emarginata (Douglas ex Hook.) D. Dietr.)) may be present (Oakley and Franklin 1998.). Evergreen low shrubs, such as Cascade barberry and salal and tall shrubs (vine maple, California hazelnut) and tall shrubs such as vine maple persist through post-disturbance sprouting. California blackberry may greatly increase in cover to dominate the ground layer. Red elderberry, (Sambucus racemosa L), willow species (Salix L.), snowbrush ceanothus (Ceanothus velutinus Douglas ex Hook), redstem ceanothus (Ceanothus sanguineus Pursh) and thimbleberry (Rubus parviflorus Nutt.) are native early seral shrubs that may be present (Halpern 1988, Brown et al. 2013). Snowbrush ceanothus can dominate on drier sites after burning. Non-native shrubs such as Scotch broom (Cytisus scoparius (L.) Link) may be present in low to moderate cover. Many late seral herb species recover and persist. Early seral native species such as fireweed (Chamerion angustifolium (L.) Holub), and Canadian horseweed (Conyza canadensis (L.) Cronquist) may be ephemeral dominants (Halpern 1989). Bull thistle (Cirsium vulgare (Savi) Ten), woodland ragwort (Senecio sylvaticus L.) and slender false brome (Brachypodium sylvaticum (Huds.) P. Beauv.), non-native herbs, may dominate the understory if seed source is present (Halpern 1988, Halpern 1989, McCain and Diaz 2002). CP1.2 Douglas-fir / vine maple-evergreen shrubs - California blackberry / forbs Grass, forbs, seedlings, single layered, open canopy Age class: 1-15

Community 1.3
Douglas-fir / evergreen shrubs / forbs

This mid-seral phase is the result of growth from CP 1.2. Large to giant decayed snags from previous disturbances may persist in this phase, although low levels of small snags may be more common. Down wood is variable, with high levels possible in post-fire generated conditions (Mellen-McLean et al. 2017). The live canopy has simple structure, dominated by sapling to pole sized trees, with some stands displaying some large to giant pre-disturbance legacy trees. Douglas-fir likely dominates, with scattered western redcedar, western hemlock and bigleaf maple present to varying degrees dependent on site conditions. Canopy cover is moderate to high due to the high tree density, especially in some post-fire conditions. This results in minimal to no tree regeneration and very low to moderate cover of shrub and herbs. On heavily burned sites snowbrush ceanothus may continue to dominate the shrub layer, resulting in lower tree density (Brown et al. 2013). Evergreen low shrubs, such as Cascade barberry and salal and tall shrubs (vine maple, California hazelnut) may be found, especially in pockets and gaps in high cover stands. Native red elderberry, willow species, snowbrush ceanothus and non-native scotch broom may be present in lower cover stands. Native herbs will persist, and non-native bull thistle and slender false brome may continue to inhabit this phase. CP1.3 Douglas-fir / evergreen shrubs / forbs Sapling/pole-sized, single layered, moderate-closed canopy Age class:15-50

Community 1.4
Douglas-fir / evergreen shrubs / western swordfern - forbs

Growth from CP1.3 produces this community phase. Large and giant snags and down wood from previous disturbances are likely present but declining in abundance due to decay and fragmentation. Smaller snags are being created from background mortality due to competition, insects, and pathogens (Mellen-McLean et al. 2017). Forest structure is still simple and largely single layered, although some multi-layered development may be beginning to be expressed in scattered openings. Canopy cover is high and dominated by small to medium sized Douglas-fir. Some legacy large and giant trees may be present in some cases. Scattered western hemlock, western redcedar and big leaf maple may be present as well. Regeneration is minimal to none. Evergreen shrubs, such as Cascade barberry and salal and tall shrubs (vine maple, California hazelnut) may be found in pockets and gaps. Herbs are varied depending on understory light levels. Under very low light levels western swordfern may be the only understory species present.

Community 1.5
Douglas-fir - western hemlock / evergreen shrubs / forbs

This phase is the result of moderate severity fire or moderate thinning of CP 1.4. Small to medium sized Douglas-fir dominate the overstory canopy layer. Large and giant snags and down wood from previous disturbances are likely present but declining in abundance due to decay and fragmentation. Small and medium snags in varying densities may result from fire and may lead to later recruitment of down wood. (Mellen-McLean et al. 2017). A range of shade tolerant (western hemlock, western redcedar, big leaf maple) and shade intolerant (Douglas-fir) trees may be present, depending on the severity and size of the disturbance (Tepley et al. 2013). Regeneration may also include shade tolerant and intolerant species. Shrub species are varied, with evergreen shrubs such as Cascade barberry and salal and tall shrubs (vine maple, California hazelnut) persisting due to sprouting adaptation. Native and non-native herbs are present, dependent on seed source and disturbance severity. CP1.5 Douglas-fir - western hemlock / evergreen shrubs / forbs Small/Med, multi layered, open to closed canopy, abundant diverse sized gaps, regenerating shade intolerant and tolerant Age class: 50-150 years

Pathway 1.1a
Community 1.1 to 1.2

Stand replacing fire is the most common pathway from this condition. Timber management, large scale wind or insects and pathogens may also return this phase to an early seral condition.

Pathway 1.2a
Community 1.2 to 1.3

Growth is the major process transitioning out of this early seral condition.

Pathway 1.3a
Community 1.3 to 1.4

Growth is the major process transitioning out of this phase. Pre-commercial thinning may also serve to change phases.

Pathway 1.4a
Community 1.4 to 1.1

Growth will serve to transition this phase into the reference condition.

Pathway 1.4c
Community 1.4 to 1.2

Regeneration harvest or stand replacing fire can return this phase back to early seral conditions.

Pathway 1.4b
Community 1.4 to 1.5

Management actions such as thinning can trigger a shift in phases. Mixed severity fire can also result in a transition to more diverse stand conditions.

Pathway 1.5a
Community 1.5 to 1.1

Growth will serve to transition this phase into the reference condition.

Pathway 1.5b
Community 1.5 to 1.2

Regeneration harvest or stand replacing fire can return this phase back to early seral conditions.

Additional community tables

Supporting information

Other references

Brown, Martin J., Jane Kertis and Mark H. Huff. 2013. Natural tree regeneration and coarse woody debris dynamics after a forest fire in the western Cascade Range. USDA Forest Service Pacific Northwest Research Station Research Paper PNW-RP-592.
Franklin, J.F., and T.A. Spies. (1991). Composition, function, and structure of old-growth Douglas-fir forests. p. 71-80. In Ruggiero, L.F.; Aubry, K.B.; Carey, A.B.; Huff, M.H. (ed.) Wildlife and vegetation of unmanaged Douglas-fir forests. Gen. Tech. Rep. PNW-GTR-285. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station. https://doi.org/10.2737/PNW-GTR-285
Halpern, Charles B. 1988. Early successional pathways and the resistance and resilience of forest communities. Ecology 69(6):1703-1715.
Halpern, Charles B. 1989. Early successional patterns of forest species: interactions of life history traits and disturbance. Ecology. 70(3): 704-720.
McCain, Cindy and Nancy Diaz. 2002. Field guide to the forested plant associations of the westside central Cascades of northwest Oregon. United States Department of Agriculture Forest Service Pacific Northwest region Technical Paper R6-NR-ECOL-TP-02-02. 403 pp.
Mellen-McLean, Kim, Bruce G. Marcot, Janet L. Ohmann, Karen Waddell, Elizabeth A. Willhite, Steven A. Acker, Susan A. Livingston, Bruce B. Hostetler, Barbara S. Webb, and Barbara A. Garcia. 2017. DecAID, the decayed wood advisor for managing snags, partially dead trees, and down wood for biodiversity in forests of Washington and Oregon. Version 3.0. USDA Forest Service, Pacific Northwest Region and Pacific Northwest Research Station; USDI Fish and Wildlife Service, Oregon State Office; Portland, Oregon. https://apps.fs.usda.gov/r6_DecAID
Moldenke, A., M. Pajutee, and E. Ingham. (2000). The functional roles of forest soil arthropods: the soil is a lively place. p. 7-22. In Powers, R.F., & Nakamura, G.M. (tech. coord.) Proceedings of the California Forest Soils Council conference on forest soils biology and forest management. Sacramento, CA. 23-24 February 1996. USDA Forest Service Gen. Tech. Report PSW-GTR-178. https://www.fs.fed.us/psw/publications/documents/gtr-178/gtr-178-ch1.pdf
Morrison, Peter H., and Frederick J. Swanson. 1990. Fire history and pattern in a Cascade Range landscape. USDA Forest Service Pacific Northwest Research Station General Technical Report PNW-GTR-254, 77 pp.
Noller, J., C. Ringo, K. Bennett, J. Hobson, and S. Hash. (2016). Landtype Associations of the Pacific Northwest National Forests. [Online]. Available at https://ecoshare.info/projects/landtype-associations/ (accessed on 5/1/2020).
Oakley, B.B. and J.F. Franklin. 1998. Bitter cherry (Prunus emarginata) distribution, successional dynamics, and implications for the role of the seed bank. Can. J. Bot. 76: 1725-1732
Orr, E., W. Orr, and E. Baldwin. (1992). Cascade Mountains. p. 141-166. In Geology of Oregon. 4th ed. Kendall/Hunt Publishing Company.
Rand, David. (2020). O horizon patterns in Oregon forest soils. Oregon Society of Soil Scientists Winter Meeting, 29 Feb 2020, Silver Falls Conference Center, Sublimity, OR. Oral presentation and slideshow.
Soil Survey Staff. (2014). Keys to Soil Taxonomy, 12th ed. USDA-Natural Resources Conservation Service, Washington, DC.
Spies, T.A., P.F. Hessburg, C.N. Skinner, K.J. Puettmann, M.J. Reilly, R.J. Davis, J.A. Kertis, J.W. Long, and D.C. Shaw. (2018). Old growth, disturbance, forest succession, and management in the area of the Northwest Forest Plan. p. 95-243. In T.A. Spies, P.A. Stine, R. Gravenmier, J.W. Long, and M.J. Reilly (tech. coords.) Synthesis of science to inform land management within the Northwest Forest Plan area. Gen. Tech. Rep. PNW-GTR-966. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station. https://www.fs.fed.us/pnw/pubs/pnw_gtr966_chapter3.pdf
Tepley, Alan J., Frederick J. Swanson, and Thomas A. Spies. 2013. Fire-mediated pathways of stand development in Douglas-fir/ western hemlock forests of the Pacific Northwest, USA. Ecology, 94(8), 2013, pp. 1729–1743.

Approval

Kirt Walstad, 2/29/2024

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	10/05/2023
Approved by	Kirt Walstad
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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