Ecological dynamics
Ecological Dynamics of the Site
This ecological site is found in cool, moderately dry mid-elevation areas, generally on moderate to steep slopes that span the lower subalpine zone. While primary data was collected in Glacier National Park (NP), this ecological site also spans into the adjacent US Forest Service (USFS) land of Flathead National Forest (FS).
Management
Various management strategies can be employed for this ecological site, depending upon the ownership of the particular land and which value is prioritized. The management of the forest determines the composition of the stand and the amount of fuel loading. A stand will be managed differently and look differently if it is managed for timber or ecological services like water quality and quantity, old growth, or endangered species. If a stand is managed for timber, it may be missing certain attributes necessary for lynx habitat. If a stand is managed for lynx habitat, it may have increased fuels and therefore an increased risk of wildfires.
The USFS Habitat Type guide states that the basal area on the west side of the Continental Divide for subalpine fir/beargrass habitat type (which relates to this ecological site) is 188+/- ft2 per acre, and the site index at 50 years for Picea is 56 feet and Abies is 47+/-6 feet. Timber production on these sites varies from low to high. Watershed management must consider the effects of southerly aspects, moderately high precipitation with high evapotranspiration, and runoff rates. Snowpack can melt periodically in the winter and disappear in spring several weeks earlier than adjacent areas. The management of USFS lands is encompassed in the “management plan” for each National Forest. The management plan for the Flathead NF also has an Appendix B that gives specific management guidelines for habitat types (which relate to our forested ecological sites) found on the forest in relation to current and historic data on forest conditions (Flathead NF Plan, 2001 and Appendix B). Another guiding USFS document is the Green et al. document (2005) which defines “Old Growth” forest for the northern Rocky Mountains. This document provides an ecologically-based classification of old growth based on forest stand attributes including numbers of large trees, snags, downed logs, structural canopy layers, canopy cover, age, and basal area. While this document finds that the bulk of the pre-settlement upland old growth in the northern Rockies was in the lower elevation, ground fire-maintained ponderosa pine/western larch/Douglas-fir types (Losensky, 1992), it does not mean that other types were not common or not important. This could apply to some of the areas of this ecological site.
The USFS Habitat Type subalpine fir/beargrass (ABLA/XETE) is common on the Flathead NF, located just west of Glacier NP. The following is a personal communication with a silvicultural forester on management of this on the Flathead NF.
Cool and Moderately Dry HTs (ABLA/XETE)
I don’t have too much experience in this habitat type. It may be too cold and dry to push western larch. Douglas fir would be a favored seral if there is no root disease. Manage lodgepole pine stands at densities to withstand mountain pine beetle populations. Even-aged management favored due to the ecology of lodgepole pine. I have seen leave islands in clearcuts (before my time) on the Tally Lake RD intended to mimic unburned areas in a stand replacement fire for wildlife cover.
State 1.0
Subalpine fir (Abies lasiocarpa) and, to a lesser amount, Engelmann spruce (Picea engelmannii), are the dominant overstory species with lodgepole pine (Pinus contorta) and Douglas-fir (Pseudotsuga menziesii) as the seral dominants with lesser amounts of western larch (Larix occidentalis) and western white pine (Pinus monticola). Whitebark pine (Pinus albicaulis) may be present, but these sites are not cold enough to give it a competitive advantage and therefore it is a minor component. The main understory species is the indicator species beargrass (Xerophyllum tenax), with the medium-sized shrub thinleaf huckleberry (Vaccinium membranaceum), grouse whortleberry (Vaccinium scoparium), and minor amounts of Oregon boxleaf (Paxistima myrsinites) and other understory species of pinegrass (Calamagrostis rubescens), Geyer’s sedge (Carex geyeri), broadleaf arnica (Arnica cordifolia), western meadow-rue (Thalictrum occidentale), and sidebells wintergreen (Orthilia secunda). This ecological site is associated to the subalpine fir/rusty menziesia ecological site on moist exposures, subalpine fir/Hitchcock’s smooth woodrush ecological site on higher elevations, and Douglas fir/thinleaf huckleberry on drier and warmer sites. Historically, this site would have had minor amounts of western white pine as a seral species before this species was decimated by the white pine blister rust epidemic (McDonald et al., 2000).
This ecological site is described as having cool and moderately dry site conditions, with a fire return interval of 50-130 years, and with fire typically of low to moderate fire intensity. This fire regime favors species such as lodgepole pine, Douglas-fir, and western larch, although subalpine fir and Engelmann spruce dominate in later successional phases. The shorter fire return interval and moderate fire intensity allow the more fire resistant Douglas-fir to be a major successional species in many stands. Douglas-fir is also able to successfully regenerate in fire-created openings where mineral soil has been exposed. Stands that are dominated by lodgepole pine and over 80 years old tend to build fuels to become a part of large stand-replacement events encompassing thousands of acres. Stand-replacement fire occurs in patches of 200 to 2,000 hectares (McDonald et al., 2000). Stand-replacement fires generally allow lodgepole pine to regenerate although some large, thick barked Douglas-fir will often survive. Stands generally have relatively large amounts of downed woody fuel, especially in those with trees over 8 cm or 3 inches in diameter. Dense understories and live fuel also help to carry fire into the tree crowns during dry conditions. Relatively deep duff layers can form and, when dry conditions exist, aid in fire spread and mortality by heating the shallow roots of subalpine fir and Engelmann spruce.
The general post-disturbance successional phases include the stand initiation phase dominated by herbaceous and shrub species and conifer seedlings, the competitive exclusion phase of dense pole-sized mixed conifer or single seral species, the maturing forest of overstory mixed conifer trees with or without patches of regeneration and the Reference phase dominated by subalpine fir and Engelmann spruce with small gap dynamics. Underburns, which affect the understory shrub and herbaceous species and conifer regeneration the most, can occur and maintain any community phase. A stand-replacement fire in the mature forest or Reference phase would result in the stand initiation phase, with species composition of seedlings varying with site conditions and seed source. Moderate fires (or mixed severity fires) in the competitive exclusion phase would favor the more fire-resistant Douglas-fir, western larch or western white pine over lodgepole pine, Engelmann spruce, and subalpine fir. Therefore, these species would dominate the maturing forest phase for a longer period of time. After a stand-replacement fire at this stage, with serotinous lodgepole pine present, then their seedlings would dominate the seedling and competitive exclusion phases. Absence of fire will transition the competitive exclusion phase to a mature forest dominated in the overstory by a mix of conifer species. Severe fire at this stage could remove much of Douglas-fir, leaving the site to be regenerated by either serotinous lodgepole pine or remnant western larch. Severe fires that remove even western larch will return to the treeless stand initiation phase. If fire does not occur in the forest maturing phase, then this will continue into the Reference phase.
Significant fires that have occurred on the west side of the Continental Divide that affected this ecological site are the 1994 Starvation Creek fire, caused by lightning, which burned 7,202 acres in Glacier NP. The Wedge Canyon fire in 2003, which burned 30,314 acres in Glacier NP, and 53,359 total acres, was also caused by lightning. The Red Bench fire in 1988 burned 27,500 acres in Glacier NP and 36,037 total acres, and also was started by lightning. The 2003 Robert fire was caused by humans and burned 52,747 acres, 39,384 of which were in Glacier NP. The Rampage fire, caused by lightning in 2003, burned 21,630 acres in Glacier NP and the 1994 Adair fire burned 9,753 acres in Glacier NP. The Wolf Gun fire in 2003 burned 14,663 acres in Glacier NP.
Both subalpine fir and Engelmann spruce are subjected to a variety of diseases and insect pests including root rot, stem decay, bark beetles, and wood borers and defoliators. These can weaken and or kill trees, which results in small openings scattered throughout the forest, or major mortality during an outbreak such as western spruce budworm (Choristoneura occidentalis). The patterns of damage from endemic populations of insects and disease creates small openings, whereas epidemic patterns are extensive throughout the landscape. Windthrow commonly can cause additional damage to stands following disease and pest disturbance. Subalpine fir is most commonly susceptible to Armillaria and Annosus root disease, pouch, Indian paint, and red belt fungi which cause stem decay, metallic, roundheaded and western balsam bark beetle, fir canker, and defoliators such as Delphinella shoot blight, black mildew, brown felt blight, fir needlecast, snow blight, and fir-blueberry rust. Engelmann spruce is most commonly susceptible to Annosus and Schweinitzii root disease and butt rot, pini rot, stem decays by red belt fungus, metallic and roundheaded borers, spruce beetle, blue stain of sapwood, spruce broom rust, spruce canker, and brown felt blight.
Aerial photography is a good tool to use to discern the level of insect and disease and the damage patterns and whether these are at endemic or epidemic levels. These maps capture only moments in time and infestations grow and move from location to location following their preferred habitat, so repeated photography can be necessary. Specifically for the northern region, the USFS Stand Health map (Aerial Detection Survey maps) shows that the major impact is defoliation by western spruce budworm. The defoliation was categorized as mostly low severity (equal to or less than 50 percent defoliation) and some as high severity (with greater than 50 percent defoliation) on Abies species, and the damage is contiguous or nearly continuous. The forest type was categorized as western Fir-Spruce type. There also was defoliation by western spruce budworm on Douglas-fir, but to a much lesser degree. Larch casebearer, a defoliator of western larch and generalized needlecast of western larch, also was found to a much lesser degree. Scattered small areas were found throughout the region including mortality from mountain pine beetle on lodgepole pine, Douglas-fir beetle on Douglas-fir, spruce beetle on Engelmann spruce, fir engravers and Woolly adelgid on ABIES spp., and general subalpine fir mortality. Both of these would affect this ecological site, and field notes corroborate these findings.
Community Phase 1.1
Subalpine fir (Engelmann spruce) /Utah honeysuckle/thinleaf huckleberry/beargrass-Western meadowrue.
Structure: multistory with small gap dynamics
The overstory is dominated by Subalpine fir and Engelmann spruce with small gap dynamics in which small numbers of trees are dead and conifer regeneration is infilling. The canopy cover ranges from 30-60 percent. At these higher elevations, both tree species are slow-growing and infill can take several decades, sustaining the multistory structure of this community. The presence of root rot pockets can shift the composition of this community away from its host species. The understory of this ecological site has an indicator species, beargrass, and usually this is dominant or at least co-dominant with thinleaf huckleberry. Species that have high frequency and canopy cover include: beargrass, thinleaf huckleberry, fireweed, Utah honeysuckle and western meadowrue (7 sites canopy cover data). Foliar cover at two sites of this ecological site is high (59%), and soil surface is predominantly duff (53.5%) and moss (44%). This is a multi-storied forested ecological site with trees ranging 7-18 m (23-60 feet) tall, a tall shrub layer approximately 102cm (40 inches) tall including Sitka alder, Utah honeysuckle, a lower layer 38-51 cm or 15-20 inches tall including beargrass and thinleaf huckleberry and the lower layer of diverse forbs less than 15 cm or 6 inches tall. The understory of this community has the medium-statured thinleaf huckleberry and a variety of other shrubs in clumps. This ecological site must have a presence of beargrass and sometimes this is dominant. At this phase Armillaria root rot and defoliation by western spruce budworm can be a threat.
Community Phase Pathway 1.1A
This pathway represents a larger disturbance: an insect infestation, wind storm, or rot pocket would create this forest structure. Areas of regeneration would range from approximately 2 to 5 acres.
Community Phase Pathway 1.1B
This pathway represents a major stand-replacement disturbance such as a high-intensity fire, large-scale wind event, or major insect infestation.
Community Phase 1.2:
Subalpine fir-Engelmann spruce-Douglas-fir/Utah honeysuckle/thinleaf huckleberry/white spirea-Oregon boxleaf/beargrass
Structure: mosaic of mature overstory and regenerating openings
Community Phase 1.2 retains some areas that resemble Community Phase 1.1, but also contains moderate-sized (2-5 acres) openings. Subalpine fir and Engelmann spruce are both host to organisms causing root rot and heart rot, and along with windthrow these can cause large pockets of overstory mortality. These areas may take decades to become reforested, resulting in either patches of shrubs or seral species such as western larch and Douglas-fir. As the organisms slowly die off due to a lack of host trees, subalpine fir and Engelmann spruce will re-colonize these areas. This community can be prone to Armillaria root rot and western spruce budworm on fir.
Community Phase Pathway 1.2A
This pathway represents growth over time with no further significant disturbance. The areas of regeneration pass through the typical stand phases—competitive exclusion, maturation, and understory reinitiating—until they resemble the old-growth structure of the Reference Community.
Community Phase Pathway 1.2B
This pathway represents a major stand-replacement fire disturbance, such as a major insect outbreak, or major fire event, which leads to the stand initiation phase of forest development.
Community Phase 1.3:
Structure: patchy clumps of regeneration, single story
Community Phase 1.3 is a forest in the stand initiation phase, possibly with scattered remnant mature trees; the composition of the seedlings depends upon the natural seed sources available. The canopy cover generally is less than 10 percent as a mixture of conifers including Douglas-fir, lodgepole pine, western larch, Engelmann spruce, and subalpine fir. If serotinous lodgepole seedbank is present, then this species will dominate the area.
Community Phase Pathway 1.3A
This pathway represents continued growth over time with no further major disturbance.
Community Phase 1.4: Pinus contorta (Subalpine fir-Engelmann spruce-Douglas-fir)/thinleaf huckleberry/grouse whortleberry-white spirea/beargrass
Structure: dense single story
Community Phase1.4 is a forest in the competitive exclusion phase, possibly with scattered remnant mature trees. Individual trees compete for the available water and nutrients. The canopy cover ranges from 50-80 percent. Canopy closure is very high within the areas successfully reforested, leading eventually to a diminished graminoid community, but also providing protection for those species which do well in the shade, such as prince’s pine. This community is more tolerant of Armillaria root rot due to forest stand composition, but is vulnerable to defoliation by western spruce budworm on fir. The understory at this community phase of this ecological site, generally has a shrub component usually dominated by either thinleaf huckleberry, grouse whortleberry or white spirea (9 sites of canopy cover data). Beargrass is always present and may be dominant. Species with the highest frequency include heartleaf arnica, prince’s plume, white spirea and beargrass.
Community Phase Pathway 1.4A
This pathway represents continued growth over time with no further major disturbance.
Community Phase Pathway 1.4B
This pathway represents a major stand-replacement disturbance, such as a major insect outbreak or major fire event, which leads to the stand initiation phase of forest development.
Community Phase 1.5: Subalpine fir-Engelmann spruce-Douglas-fir/Utah honeysuckle/thinleaf huckleberry/white spirea-Oregon boxleaf/beargrass
Structure: single story with few small openings
Community Phase 1.5 is a maturing forest which is starting to differentiate vertically. The canopy cover ranges from 40-60 percent and includes subalpine fir, Engelmann spruce, and Douglas fir in the overstory. The understory has clumps of thinleaf huckleberry, Oregon boxleaf shrub and beargrass. Individual trees are dying due to insects, disease, competition, or windthrow, allowing some sunlight to reach the forest floor. This allows for an increase in the understory as well as some pockets of overstory tree species regeneration. This community is prone to Armillaria root rot and western spruce budworm on fir. This ecological site has an indicator species, beargrass, and this can be dominant in the understory with a shrub component of thinleaf huckleberry, grouse whortleberry, white spirea and the tall shrubs Utah honeysuckle, Scouler’s willow, Rocky mountain maple. Species with the highest frequency include: prince’s plume, western rattlesnake plantain, white spirea, thinleaf huckleberry and beargrass (canopy cover data 13 sites).
Community Phase Pathway 1.5A
This pathway represents no further major disturbance. Continued growth over time, as well as ongoing mortality, leads to continued vertical diversification. The community begins to resemble the structure of the Reference Community, with small pockets of regeneration and a more diversified understory.
Community Phase Pathway 1.5B
This pathway represents a major stand-replacement fire disturbance leading to the stand initiation phase of forest development.
State 2.0
Another disease affecting this ecological site is root rot. Armillaria root disease is the most common root disease fungus in this region, especially prevalent west of the Continental Divide. It may be difficult to detect until it has killed enough trees to create large root disease pockets or centers, ranging in size from a fraction of an acre to hundreds of acres. The root disease spreads from an affected tree to its surrounding neighbors through root contact. The root disease affects the most susceptible tree species first, leaving less susceptible tree species that mask its presence. When root rot is severe, the pocket has abundant regeneration or dense brush growth in the center. In western Montana and northern Idaho, Armillaria is present in most stands with diffuse mortality and large and small root disease centers. The disease pattern is one of multiple clones merging to form essentially continuous coverage of sites. Grouped as well as dispersed mortality can occur throughout the stand. A mosaic of brushy openings, patches of dying trees, and apparently unaffected trees may cover large areas. There can be highly significant losses, usually requiring species conversion in the active management approach. Management tactics include identify the type of Armillaria root disease present, and manage for pines and larch. Pre-commercial thinning may improve growth and survival of pines and larch. Avoid harvests that leave susceptible species (usually Douglas-fir or true firs) as crop trees (Hagle, 2010). A link has been determined between parent material and susceptibility to root disease, and metasedimentary parent material is thought to increase the risk of root disease. Glacier NP is dominated by metasedimentary parent material and may be more at risk than other areas to root disease (Kimsey et al., 2012). If a stand sustains very high levels of roots disease mortality, then a coniferous stand could cross a threshold and become a shrubland, once all conifers are gone (Kimsey et al., 2012).
State 1
Current Reference State
Subalpine fir (Abies lasiocarpa) and, to a lesser amount, Engelmann spruce (Picea engelmannii), are the dominant overstory species with lodgepole pine (Pinus contorta) and Douglas-fir (Pseudotsuga menziesii) as the seral dominants with lesser amounts of western larch (Larix occidentalis) and western white pine (Pinus monticola). Whitebark pine (Pinus albicaulis) may be present, but these sites are not cold enough to give it a competitive advantage and therefore it is a minor component. The main understory species is the indicator species beargrass (Xerophyllum tenax), with the medium-sized shrub thinleaf huckleberry (Vaccinium membranaceum), grouse whortleberry (Vaccinium scoparium), and minor amounts of Oregon boxleaf (Paxistima myrsinites) and other understory species of pinegrass (Calamagrostis rubescens), Geyer’s sedge (Carex geyeri), broadleaf arnica (Arnica cordifolia), western meadow-rue (Thalictrum occidentale), and sidebells wintergreen (Orthilia secunda). This ecological site is associated to the subalpine fir/rusty menziesia ecological site on moist exposures, subalpine fir/Hitchcock’s smooth woodrush ecological site on higher elevations, and Douglas fir/thinleaf huckleberry on drier and warmer sites. Historically, this site would have had minor amounts of western white pine as a seral species before this species was decimated by the white pine blister rust epidemic (McDonald et al., 2000).
This ecological site is described as having cool and moderately dry site conditions, with a fire return interval of 50-130 years, and with fire typically of low to moderate fire intensity. This fire regime favors species such as lodgepole pine, Douglas-fir, and western larch, although subalpine fir and Engelmann spruce dominate in later successional phases. The shorter fire return interval and moderate fire intensity allow the more fire resistant Douglas-fir to be a major successional species in many stands. Douglas-fir is also able to successfully regenerate in fire-created openings where mineral soil has been exposed. Stands that are dominated by lodgepole pine and over 80 years old tend to build fuels to become a part of large stand-replacement events encompassing thousands of acres. Stand-replacement fire occurs in patches of 200 to 2,000 hectares (McDonald et al., 2000). Stand-replacement fires generally allow lodgepole pine to regenerate although some large, thick barked Douglas-fir will often survive. Stands generally have relatively large amounts of downed woody fuel, especially in those with trees over 8 cm or 3 inches in diameter. Dense understories and live fuel also help to carry fire into the tree crowns during dry conditions. Relatively deep duff layers can form and, when dry conditions exist, aid in fire spread and mortality by heating the shallow roots of subalpine fir and Engelmann spruce.
The general post-disturbance successional phases include the stand initiation phase dominated by herbaceous and shrub species and conifer seedlings, the competitive exclusion phase of dense pole-sized mixed conifer or single seral species, the maturing forest of overstory mixed conifer trees with or without patches of regeneration and the Reference phase dominated by subalpine fir and Engelmann spruce with small gap dynamics. Underburns, which affect the understory shrub and herbaceous species and conifer regeneration the most, can occur and maintain any community phase. A stand-replacement fire in the mature forest or Reference phase would result in the stand initiation phase, with species composition of seedlings varying with site conditions and seed source. Moderate fires (or mixed severity fires) in the competitive exclusion phase would favor the more fire-resistant Douglas-fir, western larch or western white pine over lodgepole pine, Engelmann spruce, and subalpine fir. Therefore, these species would dominate the maturing forest phase for a longer period of time. After a stand-replacement fire at this stage, with serotinous lodgepole pine present, then their seedlings would dominate the seedling and competitive exclusion phases. Absence of fire will transition the competitive exclusion phase to a mature forest dominated in the overstory by a mix of conifer species. Severe fire at this stage could remove much of Douglas-fir, leaving the site to be regenerated by either serotinous lodgepole pine or remnant western larch. Severe fires that remove even western larch will return to the treeless stand initiation phase. If fire does not occur in the forest maturing phase, then this will continue into the Reference phase.
Significant fires that have occurred on the west side of the Continental Divide that affected this ecological site are the 1994 Starvation Creek fire, caused by lightning, which burned 7,202 acres in Glacier NP. The Wedge Canyon fire in 2003, which burned 30,314 acres in Glacier NP, and 53,359 total acres, was also caused by lightning. The Red Bench fire in 1988 burned 27,500 acres in Glacier NP and 36,037 total acres, and also was started by lightning. The 2003 Robert fire was caused by humans and burned 52,747 acres, 39,384 of which were in Glacier NP. The Rampage fire, caused by lightning in 2003, burned 21,630 acres in Glacier NP and the 1994 Adair fire burned 9,753 acres in Glacier NP. The Wolf Gun fire in 2003 burned 14,663 acres in Glacier NP.
Both subalpine fir and Engelmann spruce are subjected to a variety of diseases and insect pests including root rot, stem decay, bark beetles, and wood borers and defoliators. These can weaken and or kill trees, which results in small openings scattered throughout the forest, or major mortality during an outbreak such as western spruce budworm (Choristoneura occidentalis). The patterns of damage from endemic populations of insects and disease creates small openings, whereas epidemic patterns are extensive throughout the landscape. Windthrow commonly can cause additional damage to stands following disease and pest disturbance. Subalpine fir is most commonly susceptible to Armillaria and Annosus root disease, pouch, Indian paint, and red belt fungi which cause stem decay, metallic, roundheaded and western balsam bark beetle, fir canker, and defoliators such as Delphinella shoot blight, black mildew, brown felt blight, fir needlecast, snow blight, and fir-blueberry rust. Engelmann spruce is most commonly susceptible to Annosus and Schweinitzii root disease and butt rot, pini rot, stem decays by red belt fungus, metallic and roundheaded borers, spruce beetle, blue stain of sapwood, spruce broom rust, spruce canker, and brown felt blight.
Aerial photography is a good tool to use to discern the level of insect and disease and the damage patterns and whether these are at endemic or epidemic levels. These maps capture only moments in time and infestations grow and move from location to location following their preferred habitat, so repeated photography can be necessary. Specifically for the northern region, the USFS Stand Health map (Aerial Detection Survey maps) shows that the major impact is defoliation by western spruce budworm. The defoliation was categorized as mostly low severity (equal to or less than 50 percent defoliation) and some as high severity (with greater than 50 percent defoliation) on Abies species, and the damage is contiguous or nearly continuous. The forest type was categorized as western Fir-Spruce type. There also was defoliation by western spruce budworm on Douglas-fir, but to a much lesser degree. Larch casebearer, a defoliator of western larch and generalized needlecast of western larch, also was found to a much lesser degree. Scattered small areas were found throughout the region including mortality from mountain pine beetle on lodgepole pine, Douglas-fir beetle on Douglas-fir, spruce beetle on Engelmann spruce, fir engravers and Woolly adelgid on ABIES spp., and general subalpine fir mortality. Both of these would affect this ecological site, and field notes corroborate these findings.
Community 1.1
Reference Community
Plant Community 1.1 Reference Community
Subalpine fir (Engelmann spruce)/Utah honeysuckle/thinleaf huckleberry/beargrass-Western meadowrue.
Structure: Multistory with small gap dynamics
Tree Age: 150+ years
Community 1.2
Mature stand with patches.
Plant Community 1.2
Subalpine fir-Engelmann spruce-Douglas fir/Utah honeysuckle/Thinleaf huckleberry/white spirea-Oregon boxleaf/beargrass.
Sturcture: Mature stand with patches.
Tree Age: 0-10 and 150+ years.
Community 1.3
Patchy Clumps, Single Story
Plant Community 1.3
Structure: patchy clumps, single story.
Time spent in this phase: 20-40 years.
Community 1.4
dense single story with diminished understory
Plant Community 1.4
Pinus contorta(Subalpine fir-Engelmann spruce-Douglas fir)/
thinleaf huckleberry/grouse whortleberry-white spirea/Beargrass.
Structure: dense single story with diminished understory.
Time spent in this phase: 25-60 years
Community 1.5
vertical differentiation in stand
Plant Community 1.5
Subalpine fir-Engelmann spruce-Douglas fir/Utah honeysuckle/Thinleaf huckleberry/ white spirea-Oregon boxleaf/beargrass.
Structure: some vertical differentiation in stand.
Time spent in this phase: 20-50 years.
Pathway 1.1A
Community 1.1 to 1.2
This pathway represents a larger disturbance: an insect infestation, wind storm, or rot pocket would create this forest structure. Areas of regeneration would range from approximately 2 to 5 acres.
Pathway 1.1B
Community 1.1 to 1.3
This pathway represents a major stand-replacement disturbance such as a high-intensity fire, large-scale wind event, or major insect infestation.
Pathway 1.2A
Community 1.2 to 1.1
This pathway represents growth over time with no further significant disturbance. The areas of regeneration pass through the typical stand phases—competitive exclusion, maturation, and understory reinitiating—until they resemble the old-growth structure of the Reference Community.
Pathway 1.2B
Community 1.2 to 1.3
This pathway represents a major stand-replacement fire disturbance, such as a major insect outbreak, or major fire event, which leads to the stand initiation phase of forest development.
Pathway 1.3A
Community 1.3 to 1.4
This pathway represents continued growth over time with no further major disturbance.
Pathway 1.4B
Community 1.4 to 1.3
This pathway represents a major stand-replacement disturbance, such as a major insect outbreak or major fire event, which leads to the stand initiation phase of forest development.
Pathway 1.4A
Community 1.4 to 1.5
This pathway represents continued growth over time with no further major disturbance.
Pathway 1.5A
Community 1.5 to 1.1
This pathway represents no further major disturbance. Continued growth over time, as well as ongoing mortality, leads to continued vertical diversification. The community begins to resemble the structure of the Reference Community, with small pockets of regeneration and a more diversified understory.
Pathway 1.5B
Community 1.5 to 1.3
This pathway represents a major stand-replacement fire disturbance leading to the stand initiation phase of forest development.
State 2
Root Rot State
Another disease affecting this ecological site is root rot. Armillaria root disease is the most common root disease fungus in this region, especially prevalent west of the Continental Divide. It may be difficult to detect until it has killed enough trees to create large root disease pockets or centers, ranging in size from a fraction of an acre to hundreds of acres. The root disease spreads from an affected tree to its surrounding neighbors through root contact. The root disease affects the most susceptible tree species first, leaving less susceptible tree species that mask its presence. When root rot is severe, the pocket has abundant regeneration or dense brush growth in the center. In western Montana and northern Idaho, Armillaria is present in most stands with diffuse mortality and large and small root disease centers. The disease pattern is one of multiple clones merging to form essentially continuous coverage of sites. Grouped as well as dispersed mortality can occur throughout the stand. A mosaic of brushy openings, patches of dying trees, and apparently unaffected trees may cover large areas. There can be highly significant losses, usually requiring species conversion in the active management approach. Management tactics include identify the type of Armillaria root disease present, and manage for pines and larch. Pre-commercial thinning may improve growth and survival of pines and larch. Avoid harvests that leave susceptible species (usually Douglas-fir or true firs) as crop trees (Hagle, 2010). A link has been determined between parent material and susceptibility to root disease, and metasedimentary parent material is thought to increase the risk of root disease. Glacier NP is dominated by metasedimentary parent material and may be more at risk than other areas to root disease (Kimsey et al., 2012). If a stand sustains very high levels of roots disease mortality, then a coniferous stand could cross a threshold and become a shrubland, once all conifers are gone (Kimsey et al., 2012).
Community 2.1
Armillaria Root Rot Community
Metasedimentary and quartzite parent material (vitrandic soils on south and west aspects).
Shrubland with no trees
Time=50 years
Transition T1A
State 1 to 2
High density fir becomes infected
Restoration pathway R2A
State 2 to 1
Active management and seeding of true pine and larch species.
