Bog birch is native to North America. It is widely distributed from interior Alaska to Greenland and south through Canada to New York, Michigan, and Minnesota in the East and Colorado, New Mexico, and California in the West [51,60,66,75,76,159,168]. Flora of North America provides a distributional map of bog birch.
States or Provinces
Regional Distribution in the Western United States
This species can be found in the following regions of the western United States (according to the Bureau of Land Management classification of Physiographic Regions of the western United States):
BLM PHYSIOGRAPHIC REGIONS :
2 Cascade Mountains
4 Sierra Mountains
8 Northern Rocky Mountains
9 Middle Rocky Mountains
10 Wyoming Basin
11 Southern Rocky Mountains
16 Upper Missouri Basin and Broken Lands
Bog birch is a deciduous, long-lived shrub. Plants are low and spreading to erect with 1 to several main stems. Bog birch ranges from 8 inches (20 cm) tall on upland sites and in arctic environments to 10 feet (3 m) in drainages and in more southern areas [31,44,60,76,77,77,102,137,159,168]. The bark is thin, smooth, and does not peel readily [51,75,159,168]. Leaves are thick and leathery and range from 0.2 to 1.2 inches (0.5-3 cm) long and 0.2 to 0.8 inch (0.5-2 cm) wide [75,76,77,159]. The inflorescences are catkins. Male catkins are 0.4 to 1 inch (10-25 mm) long, and female catkins are 0.3 to 0.8 inch (7-20 mm) long [31,159,168]. Fruits are narrow-winged, single-seeded samaras 1 to 1.5 mm long and wide [31,41,104]. Rhizomes are 0.8 to 2.4 inches (2-6 cm) thick and are found in the top 2.4 inches (6 cm) of soil . Bog birch has an extensive root system [24,42,104]. Roots are ectomycorrhizal, an adaptation to arctic and alpine soils that are generally low in inorganic nitrogen and phosphorus [37,145].
Bog birch occupies a wide variety of sites, ranging from rocky subarctic and alpine tundra to deep, organic, boreal soils . It is typically a wetland species occurring most commonly on moist, acidic, and nutrient-poor organic sites including fens, swamps, bogs, muskegs, wet meadows, lake and stream margins, and seepage areas [22,31,48,60,75,76,77,159,168]. Bog birch is also found on upland sites including eskers, till ridges, rock outcrops covered with shallow soil, cliffs, sandy hillsides, and rocky ridges [5,31,51,82,137]. It dominates open valley bottoms in the Canadian Rocky Mountains  and is the most common shrub at treeline in interior Alaska, forming a nearly continuous zone between the treeline and alpine tundra in many areas .
Elevational ranges for bog birch by state or province
|Sierra Nevada||6,500-8,500 |
|Nova Scotia||1,300 |
Temperature: Bog birch is tolerant of cold temperatures. It is common in black spruce forests in the Yukon where the mean annual temperature is 27 Â°F (-3 Â°C) . Frost tolerance in bog birch is high, and bog birch grows abundantly over large areas of permafrost . Bog birch tolerates severe winter temperatures by withdrawing water from the protoplast and freezing it in the cell walls .
Moisture: Although it is primarily a wetland plant, bog birch does not appear to tolerate continuous flooding. In bogs near Fairbanks, Alaska, bog birch abundance decreases as soil moisture increases. Bog birch is also more "vigorous" in communities that support taller tussocks . In the Cariboo Forest Region of British Columbia, bog birch is common in wetlands that have no standing water late in the season . In Montana, however, the water table is often within the rooting zone of bog birch throughout the summer, and bog birch grows in soils that remain flooded until midsummer or are saturated year-round . In a willow (Salix spp.)-bog birch community near Churchill, Manitoba, the depth of the water table averaged 3 inches (6.5 cm) below the surface, and soil moisture in the organic layer was 63% . Bog birch is an indicator of "substantial groundwater" in the North Thompson River valley, British Columbia .
Annual precipitation ranges from 4 to 9 inches (109-230 mm) on 2 northern Canadian study sites where bog birch is abundant [6,24]. While some authors describe bog birch as drought intolerant , in a review of the literature de Groot and others  state that bog birch appears tolerant of periodic drought.
Soils: Bog birch grows in a variety of soils, ranging from sandy and gravelly loam on river terraces to poorly drained, organic soils in bogs, muskegs, and other wetland habitats [43,64,114,121,141]. It is tolerant of moderate salinity  and pH ranging from 3.1 to 6.5 [105,141].
Key Plant Community Associations
In the boreal forests of interior Alaska and Canada, bog birch is found in many
black spruce (Picea mariana) and white spruce (P. glauca)
communities and is especially common at the northern and altitudinal limit of
trees [3,6,117,152,154,159]. In these
northern environments, permafrost prevents the percolation of water, resulting
in the development of muskegs, bogs, and ponds that often impede the growth of
trees but support bog birch and other low-growing shrubs [55,159].
Bog birch is characteristic of many mixed shrub and tussock tundra
communities in Alaska and northern Canada [1,2,10,149]. In southwestern Canada and the contiguous United States,
bog birch often occurs on wetland sites including bogs, fens and carrs, within
lodgepole pine (Pinus contorta), Engelmann spruce (P. engelmannii),
or subalpine fir (Abies lasiocarpa) forest types and is often associated
with alders (Alnus spp.) and willows (Salix spp.) [15,22,84,86,110].
Bog birch is listed as a dominant species in the
following vegetation classifications:
black spruce/bog birch/feather moss (Hylocomium spp.) vegetation type
black spruce/bog birch-marsh Labrador tea/sphagnum (Ledum palustre/Sphagnum spp.) vegetation type
black spruce-white spruce/bog birch vegetation type 
black spruce-white spruce/bog birch/feather moss community 
black spruce-white spruce/bog birch/reindeer lichen (Cladonia spp.) community 
black spruce-white spruce/thinleaf alder (Alnus incana ssp. tenuifolia)-bog birch/Schreber's big
red stem moss (Pleurozium schreberi) vegetation type
bog birch vegetation type
bog birch-blueberry/rough fescue (Vaccinium spp./Festuca altaica)/feather moss-lichen vegetation type
bog birch-blueberry/Bigelow's sedge (Carex bigelowii) vegetation type
bog birch-bog blueberry-black crowberry (Vaccinium uliginosum-Empetrum nigrum)-
marsh Labrador tea/lichen vegetation type
bog birch-bog blueberry/sedge (Carex spp.)/sphagnum vegetation type
bog birch-bog rosemary (Andromeda polifolia)/sphagnum vegetation type
bog birch-diamondleaf willow (Salix planifolia)-bog blueberry vegetation type
- bog birch-Lapland rosebay (Rhododendron lapponicum)/sedge vegetation type
bog birch-mountain cranberry-cloudberry (Vaccinium vitis-idaea-Rubus chamaemorus)/sphagnum vegetation type
bog birch-marsh Labrador tea-blueberry vegetation type
bog birch-marsh Labrador tea/mountain cranberry/wideleaf polargrass (Arctagrostis latifolia) vegetation type
bog birch/Schreber's big red stem moss-mountain-fern moss (H. splendens) vegetation type
bog birch-sweet gale (Myrica gale)-bog rosemary/sphagnum vegetation type
bog birch-sweet gale/sedge/sphagnum vegetation type
bog birch-willow (Salix spp.)-marsh Labrador tea/Bigelow's sedge/feather moss-lichen vegetation type
bog birch-willow-thinleaf alder vegetation type
mountain alder (Alnus viridis subsp. crispa)-bog birch-marsh Labrador tea/sphagnum vegetation type
paper birch/bog birch/feather moss vegetation type
shrubby cinquefoil (Dasiphora fruticosa ssp. floribunda)-
sweet gale-bog birch-black crowberry/sphagnum vegetation type
shrubby cinquefoil-sweet gale-bog birch-marsh Labrador tea/feather moss vegetation type
white spruce/bog birch/feather moss-reindeer lichen vegetation type
white spruce/bog birch/reindeer lichen vegetation type
white spruce/bog birch/sphagnum vegetation type
white spruce/bog birch/mountain-fern moss vegetation type 
diamondleaf willow-bog birch shrub association 
willow-bog birch type 
Wolf's willow (S. wolfii)-bog birch-shrubby cinquefoil shrub association 
bog birch/woollyfruit sedge (C. lasiocarpa) community type 
bog birch dominance type 
bog birch/tufted hairgrass (Deschampsia caespitosa) community type 
bog birch/woollyfruit sedge community type 
grayleaf willow (S. glauca)-bog birch-shrubby cinquefoil shrub type 
bog birch-kinnikinnick (Arctostaphylos uva-ursi) shrub carr association 
white spruce/willow (Salix spp.)-bog birch zone 
bog birch/star reindeer lichen (Cladonia alpestris)-moss community (Kershaw 1984, cited in )
birch (Betula spp.) vegetation association 
balsam poplar (Populus balsamifera)/bog birch/arctic lupine (Lupinus arcticus) vegetation type
black spruce/bog birch-marsh Labrador tea vegetation type 
bog birch/rough fescue community 
bog birch-bog blueberry-reindeer lichen vegetation type
cloudberry-bog birch-bog blueberry vegetation type
lichen-bog birch-marsh Labrador tea vegetation type 
white spruce/bog birch/water sedge (Carex aquatilis) community 
Habitat: Rangeland Cover Types
This species is known to occur in association with the following Rangeland Cover Types (as classified by the Society for Range Management, SRM):
More info for the terms: cover, lichen, shrub, tundra, tussock
SRM (RANGELAND) COVER TYPES :
216 Montane meadows
410 Alpine rangeland
904 Black spruce-lichen
911 Lichen tundra
912 Low scrub shrub birch-ericaceous
913 Low scrub swamp
916 Sedge-shrub tundra
917 Tall shrub swamp
918 Tussock tundra
919 Wet meadow tundra
920 White spruce-paper birch
Habitat: Cover Types
This species is known to occur in association with the following cover types (as classified by the Society of American Foresters):
More info for the term: cover
SAF COVER TYPES :
1 Jack pine
5 Balsam fir
12 Black spruce
13 Black spruce-tamarack
107 White spruce
201 White spruce
202 White spruce-paper birch
203 Balsam poplar
204 Black spruce
206 Engelmann spruce-subalpine fir
218 Lodgepole pine
222 Black cottonwood-willow
251 White spruce-aspen
252 Paper birch
253 Black spruce-white spruce
254 Black spruce-paper birch
Habitat: Plant Associations
This species is known to occur in association with the following plant community types (as classified by Küchler 1964):
KUCHLER  PLANT ASSOCIATIONS:
K008 Lodgepole pine-subalpine forest
K012 Douglas-fir forest
K015 Western spruce-fir forest
K052 Alpine meadows and barren
K093 Great Lakes spruce-fir forest
K094 Conifer bog
This species is known to occur in the following ecosystem types (as named by the U.S. Forest Service in their Forest and Range Ecosystem [FRES] Type classification):
FRES10 White-red-jack pine
FRES26 Lodgepole pine
Fire Management Considerations
Prescribed burning can reduce bog birch cover. Naturally occurring fires controlled the spread of bog birch on Canadian Rocky Mountain rangelands prior to active fire exclusion. Today, prescribed fires are used to reduce the spread of bog birch and other shrubs and to restore and maintain native grasslands . The effects of prescribed burning on bog birch vary depending on burning conditions, fire season, severity, and postfire growing conditions. Burning bog birch stands in spring, when carbohydrate reserves are lowest, apparently promotes postfire sprouting and growth. Increased fire severity and fall burning both increase mortality in bog birch .
Prescribed burning at 3- to 6-year intervals in the Rocky Mountain foothills of Alberta has decreased shrub cover and increased forage production . Bog birch cover decreased by 35% following a moderate-severity, prescribed spring fire in wood bison habitat in Fort Providence, Northwest Territories. After 3 months, bog birch cover increased by 26% . Due to bog birch's "vigorous" sprouting response, burning at regular intervals is necessary to minimize its regrowth .
|Moisture content (%) of bog birch in dry and wet tundra |
|18 July||1 August||15 August|
In very wet places bog birch stands act as natural fire breaks .
Plant Response to Fire
Fire has a substantial influence on bog birch growth and population dynamics [43,44]. Bog birch survives most low- and moderate- severity fires by sprouting from the root crown and/or rhizomes after top-kill by fire [43,44,82,112,165]. It flowers "profusely" from young sprouts  and produces large leaves after burning. Bog birch leaves were up to 3 times larger 1 year after fire than leaves on unburned plants near Inuvik, Northwest Territories, a response that may be linked to the increase in available nutrients following the fire [164,165]. A large proportion of phosphorus released into the soil after fire is absorbed by the roots of bog birch and then incorporated into new stem and leaf tissue. Changes in bog birch root biomass, root phosphorus concentration, and root phosphorus mass with burning of a mature 140-year-old black spruce/star reindeer lichen woodland at Schefferville, Quebec, were as follows :
|Changes in root biomass and root phosphorus in bog birch before and after fire |
|Root characteristics||Mature (140-year-old)||Burned (0-year-old)||Change (%)|
|root biomass (kg/ha)||9,159||8,886||-4|
|concentration of P in roots (% dry weight)||0.047||0.133||+283|
|mass of P in roots (kg/ha)||4.30||11.80||+274|
Bog birch increases after low- to moderate-severity fires . Repeated fires near treeline and on some wet sites in Alaska and northern Canada result in thickets of bog birch, mountain alder, and willows (Salix spp.) [82,154]. On tundra sites near Inuvik, Northwest Territories, total vascular plant cover on a burned area was more than twice that on an adjacent unburned area. The increase was due in large part to bog birch, which increased 8.8% after the burn .
Because of its ability to sprout from the root crown and rhizomes, bog birch is among the first plants to regenerate after fire in many communities [26,43,44,69,105,149,150]. Bog birch also persists into middle and late successional stages [23,105,133,149,150]. It was present in all postfire successional stages observed in a black spruce/reindeer lichen woodland in northern Quebec, but was most abundant in the intermediate stages between approximately 20 and 50 years after fire . Frequency of bog birch at each successional stage is summarized below.
|Frequency (%) of bog birch at 4 postfire stages |
|postfire year 5||postfire year 20||postfire year 50||postfire year 90|
In subarctic black spruce forests of western Labrador, bog birch was most abundant 18 to 40 years after fire. Mean canopy volume of bog birch between 2 and 140 years after fire is summarized below .
|Mean canopy volume (mÂ³) of bog birch across 5 postfire successional stages |
|postfire year 2||postfire year 18||postfire year 40||postfire year 80||postfire year 140|
Low-severity fire and spring burning promote sprouting in bog birch. In a study conducted during the 1992 growing season in the Rocky Mountains of Alberta, bog birch plants were burned in low-, medium-, and high-severity treatments. Plants burned earlier in the growing season and in low-severity treatments produced more and taller sprouts by the end of the first year after burning than plants burned late in the growing season or in severe fire treatments. Bog birch in the high-severity treatments sprouted latest. Following high-severity fire, new sprouts originated from the bottoms of rhizomes, indicating mortality of buds closer to the soil surface. No sprouting occurred on plants burned after late June, which may be related to seasonal variation in plant hormones that release buds from dormancy and promote stem extension in bog birch. Fall burning resulted in greatest plant mortality than spring and summer burning. Some plants burned in the fall sprouted the following year [43,44].
Bog birch was more abundant in "lightly" burned areas than in "heavily" burned areas following a June 1971 wildfire in black spruce forest near Fairbanks, Alaska . Density of bog birch for 4 years following the fire is provided below.
|Bog birch density (stems/ha) after wildfire in heavily and lightly burned areas |
|postfire year 1||postfire year 2||postfire year 3||postfire year 4|
The response of bog birch to fire in a valley-bottom floodplain in the Rocky Mountains of Alberta varied with fire severity. Bog birch stem density increased for 2 years after a spring prescribed, low-severity fire in 1984 due to abundant sprouting. Following high-severity burns in 1987 and 1993, however, both stem density and canopy cover sharply declined. Results of this study are given in the figure below .
On some sites, including in Wisconsin fens, bog birch increases in the absence of fire . In the Rocky Mountains of Alberta, bog birch forms extensive, closed-canopy stands where fire has been excluded .
Immediate Effect of Fire
Bog birch is easily top-killed by fire due to its thin bark, small stem diameter, and resinous, flammable twigs [44,77,159]. Both young and old bog birch plants are susceptible to top-kill by fire . High-severity fire can kill bog birch plants by heating or consuming organic soil layers and scorching root crowns, rhizomes, and roots [93,169]. Seeds are easily killed by fire .
POSTFIRE REGENERATION STRATEGY :
Small shrub, adventitious buds and/or a sprouting root crown
Rhizomatous shrub, rhizome in soil
Initial off-site colonizer (off site, initial community)
Fire adaptations: Bog birch can survive low- to moderate-severity fires. On many sites, bog birch has deep roots and rhizomes that are protected from all but high-severity fires [12,42]. Bog birch regenerates after fire by sprouting from the root crown and from dormant buds on the rhizomes [43,44,82,112,165]. In arctic and boreal ecosystems, bog birch increases sprout production, sprout height, and aboveground biomass production during the first 1 to 2 years after a fire. Bog birch responds to top-kill by sprouting from dormant buds on the root crown and rhizomes after top-kill release. Burned plants may produce large leaves that senesce later in the fall than leaves on undisturbed plants, thereby maximizing photosynthate production . Bog birch samaras are dispersed by wind and can invade burned areas from off site . Although bog birch can establish from seed after fire, seedlings are susceptible to both drought and shade [43,44].
FIRE REGIMES: Bog birch is adapted to a wide range of FIRE REGIMES, from subarctic and alpine areas that seldom burn to boreal environments that burn frequently [42,44]. Wetland areas where bog birch grows burn infrequently due to the high moisture content of the vegetation and soil. These sites sometimes act as firebreaks. Fires do occur, however, during dry summers or in the spring and fall when the vegetation is dry [35,43,44,86,104,143].
In interior Alaska, bog birch is found on poorly drained and permafrost underlain sites occupied primarily by black spruce stands, muskegs, and bogs. These types are widespread in Alaska and burn frequently [154,158]. Black spruce-birch (Betula spp.) is the most widespread forest type in interior Alaska and also the type with the highest frequency of fire . Native Americans were an important cause of fires in the black spruce-birch ecosystem . Fire frequency increased with the increase in mining activity in the 1800s . Today, most fires are lightning caused [70,95]. Between 1940 and 1969, lightning was responsible for 78% of the area burned in interior Alaska .
Fires occur in interior Alaska between 1 April and 30 September. Most fires occur in May, June, and July, corresponding with the highest annual temperatures, longest day length, lowest humidity and precipitation, and high winds [55,154]. Fires can occur, however, whenever fuels are not covered with snow and are exposed to sufficiently warm temperatures and drying winds .
Fire years are sporadic in occurrence but tend to occur at least once every decade . ÂExceptional fire yearsÂ are characteristic of the black spruce-birch ecosystem. In Alaska, 6 years (1941, 1950, 1957, 1969, and 1977) accounted for 63% of the total area burned between 1940 and 1978 . The average acreage burned each year in interior Alaska is approximately 1 million acres . Fires tend to be large and may spread over thousands to hundreds of thousands of acres or more [71,94,150].
Estimated fire-return intervals in the black spruce-birch ecosystem vary from 50 to 200 years [71,160]. Fires occur every 50 to 70 years in black spruce-white spruce/bog birch/reindeer lichen communities in interior Alaska . Heinselman  estimates a fire-return interval of 130 years for open black spruce/reindeer lichen forest and 100 years for closed-canopy black spruce forest. Mean fire-return intervals in lowland black spruce forests on the Kenai Peninsula, Alaska, range from 89 to 195 years [4,97].
Black spruce-birch communities experience high-severity, stand-replacing fires. These communities are highly flammable due to the abundance of ericaceous shrubs, the prevalence of dead, low-hanging branches on the black spruce trees, which are often covered with highly flammable epiphytic lichens, and the thick moss and lichen mats that cover the forest floor and become highly flammable after periods of low rainfall [94,95,155]. There is often nearly continuous fuel from the forest floor to the tree crowns . Most fires in black spruce-birch communities are either crown fires or ground fires severe enough to damage or kill aboveground vegetation, including overstory trees. Fires may be severe enough to completely expose the mineral soil layer [50,71,150,160].
The following table provides fire return intervals for plant communities and ecosystems where bog birch is important. For further information, see the FEIS review of the dominant species listed below.
|Fire-return intervals for plant communities with bog birch|
|Community or Ecosystem||Dominant Species||Fire Return Interval Range (years)|
|birch||Betula spp.||80-230 |
|tamarack||Larix laricina||35-200 |
|Great Lakes spruce-fir||Picea-Abies spp.||35 to >200|
|northeastern spruce-fir||Picea-Abies spp.||35-200 |
|Engelmann spruce-subalpine fir||Picea engelmannii-Abies lasiocarpa||35 to >200 |
|black spruce||Picea mariana||35-200|
|conifer bog*||Picea mariana-Larix laricina||35-200 |
|jack pine||Pinus banksiana||<35 to 200 [34,50]|
|Rocky Mountain lodgepole pine*||Pinus contorta var. latifolia||25-340 [16,17,144]|
|aspen-birch||Populus tremuloides-Betula papyrifera||35-200 [50,161]|
|quaking aspen (west of the Great Plains)||Populus tremuloides||7-120 [7,62,103]|
|Rocky Mountain Douglas-fir*||Pseudotsuga menziesii var. glauca||25-100 [7,8,9]|
More info for the terms: bog, climax, cover, frequency, shrub, tundra
Bog birch is shade intolerant [42,44,87]. It is characteristic of canopy openings in black spruce woodlands in boreal Canada . It establishes from seed or, more commonly, by sprouting after fire and other disturbances [23,43,148,149] and in many communities persists through subsequent successional stages. In many black spruce communities in central Alaska and northern Canada, bog birch appears soon after low- to moderate-severity fires and is dominant in the vegetation 6 to 25 years after fire. Trees begin to dominate after 25 to 30 years, but the low shrub layer of bog birch and associated species continues to expand and increase in cover [149,150]. In black spruce woodlands in the Northwest Territories, bog birch is most common 15 to 20 years after fire but is also present in stands as old as 300 years .
The table below summarizes an analysis of 5 stands representing a vegetation chronosequence on gravel outwash of the Muldrow Glacier in Denali National Park, Alaska. Bog birch was not present in the earliest successional stage but was abundant in intermediate stages and persistent in the oldest stands .
|Frequency (%) and cover (%) of bog birch at 5 successional stages |
|Pioneer stage (25-30 years)||0||0|
|Meadow stage (100 years)||80||<5|
|Early shrub stage (150-200 years)||100||50-75|
|Late shrub stage (200-300 years)||100||50-75|
|Climax tundra (5,000-9,000 years)||100||25-50|
Bog birch reproduces by seed and vegetatively by branch layering and sprouting [26,44]. Reproduction by seed is more common in southern populations, and vegetative reproduction is more common in northern populations [73,166,167].
Pollination: Bog birch is wind pollinated. In a bog birch population on Baffin Island, Northwest Territories, female catkins were smaller and contained 50% fewer flowers than were contained in female catkins from a more southern site in subarctic Quebec. There was an estimated 10-fold difference in pollen dispersed between the 2 sites. At the northern extent of its distribution, bog birch is clonal, and the distance between genetically distinct individuals is great. In these areas, female catkins are more likely to receive incompatible pollen, preventing fertilization from occurring .
Seed production: Bog birch produces numerous catkins, each of which yields 30 to 50 samaras . Seed production is generally high in more southern parts of its range [30,42,73]. In more northern areas, production of viable seed is limited by the shorter growing season, lower temperatures, and distance between genetically distinct individuals .
Seed banking: Bog birch produces numerous, tiny seeds and has a transient seed bank. In a review of the literature, Karrfalt  states that birch seeds may be abundant in the soil but the seeds are generally short lived. Rowe 1983  states that viable bog birch seeds are "rare" in the soil seed bank. Bog birch seeds were present, however, in the first 1.2 inches (3 cm) of soil collected from alpine sites on the GaspÃ© Peninsula, Quebec . Results of this study are provided in the table below.
Bog birch seed production and density on sites in Quebec 
|Site||Total seeds/mÂ²||Viable seeds/mÂ²||% cover in aboveground vegetation|
Germination: Prechilling improves germination of bog birch seeds. Optimum germination temperature for many arctic species is 59 to 86 Â°F (15-30 Â°C) . The germination rate of bog birch seeds collected from alpine sites in the White Mountains, New Hampshire, was 25% for refrigerated seeds and 4% for unrefrigerated seeds. Days required for germination ranged from 14 to 28 for refrigerated seeds and from 27 to 299 for unrefrigerated seeds .
Seed viability varies with latitude. At the northern range limit of bog birch on Baffin Island, <0.5% of seeds were viable. Very few samaras contained seeds with fully developed embryos. At a southern site in subarctic Quebec, 70% of seeds were viable [166,167]. Seeds that overwinter on plants remain viable until they disperse the following spring .
Seed germination and samara weight may be correlated. In a germination study in Kuujjuaq, Quebec, no seeds from samaras weighing <0.09 mg germinated, few samaras weighing <0.12 mg had seed that germinated, and all samaras weighing >0.34 mg had seed that germinated . Germination of wind-dispersed seeds may be highest on exposed mineral soils .
Seedling establishment/growth: Seedling recruitment rates in bog birch populations are usually very low. Site disturbance by fire increases the likelihood of seedling establishment . Although recruitment from seed is almost nonexistent in northern bog birch populations, plants of all age classes were evident in a southern Quebec population [73,166]. Seedling growth is very slow, and seedling mortality is often high [41,44].
Vegetative regeneration: Bog birch reproduces vegetatively by branch layering and sprouting from dormant buds on the root crown and rhizomes [26,44]. Bog birch is clonal in the northern parts of its range .
Growth Form (according to Raunkiær Life-form classification)
More info for the terms: chamaephyte, phanerophyte
RAUNKIAER  LIFE FORM:
Life History and Behavior
More info for the term: bog
In bog birch, leaf growth begins soon after snow melt, and growth continues throughout the growing season as shoots elongate . Male catkins develop in late summer or fall and expand with or before leaf development the following spring. Female catkins appear with the leaves in the spring [78,104]. Flowering dates vary and are summarized below.
|Flowering dates for bog birch by region|
|Sierra Nevada, California||April-June |
|GaspÃ© Peninsula, Quebec||June-August |
Fruits mature between July and October and can persist through the winter [104,106,159,166]. Samara dispersal occurs in the fall, just prior to snow fall, and in the following spring soon after snow melt [78,166]. Leaves begin to senesce in late summer, and leaf abscission is complete by late September .
Phenological stages for bog birch in a valley-bottom floodplain in west-central Alberta are summarized below.
|Seasonal development of bog birch in west-central Alberta |
|5 May||most plants initiating leaf-break|
|10 June||male catkins dropped; female catkins small and turning darker green|
|29 June||female catkins at mature size|
|11 Aug.||female catkins brown; terminal buds large|
|1 Sept.||half of leaves on most plants yellow|
Molecular Biology and Genetics
Barcode data: Betula glandulosa
Statistics of barcoding coverage: Betula glandulosa
Public Records: 14
Specimens with Barcodes: 28
Species With Barcodes: 1
Bog birch decreases with grazing. Bog birch cover was significantly (P=0.01) greater on ungrazed
sites (88%) than on grazed sites (47%) within the summer range of the
RiviÃ¨re George caribou herd in
northern Quebec and Labrador, Canada. Browsing and
trampling by caribou have opened the closed canopy of bog birch and reduced leaf
biomass by 60% . Bog birch plants heavily browsed by snowshoe hares near Kluane, Yukon,
exhibited rapid growth of new twigs when hare numbers declined .
Expanding bog birch populations
on Canadian Rocky Mountain rangelands reduce forage for elk, bison, and
other grazing animals. Removal of bog
birch increases the production of forage grasses .
Information on the effects of herbicides on bog birch is available in Chapin and others .
Relevance to Humans and Ecosystems
Value for rehabilitation of disturbed sites
The erosion control potential for bog birch is high. In Montana, the dense underground network formed by bog birch and rhizomatous sedges help stabilize streambanks . Because bog birch grows slowly, its short-term (1-3 years) revegetation potential is low. Bog birch is, however, suitable for long-term (>3 years) revegetation of exposed mineral soil [28,101].
Black spruce seedling survival after fire in the boreal forest may be facilitated by shading from bog birch and other shrubs that reproduce vegetatively and grow quickly .
Importance to Livestock and Wildlife
Bog birch is only lightly to moderately browsed by most classes of livestock [19,107]. It accounted for 2.7% of summer cattle forage, for example, on the Red Rock Lakes National Wildlife Refuge in Montana . Browse production may be moderate to high in some bog birch communities. However, cattle tend to avoid the boggy soils associated with this species unless the soil becomes dry enough to walk on, usually in late summer [40,64,86,104]. Cattle eat bog birch in riparian wet meadows in the southern Blue Mountains, Oregon .
Numerous wildlife species eat bog birch, including moose, mule deer, white-tailed deer, Rocky Mountain elk, mountain goats, caribou, grizzly bears, American black bears, small mammals, birds, and insects [14,68,74,81,91,109,126,146,159]. Bog birch is a "preferred" browse species for game animals in Teton County, Wyoming . It is dominant in tamarack swamps in southwestern Manitoba. These swamps provide habitat for moose, jumping mice, northern river otters, shrews, Canada jays, black-capped chickadees, white-throated sparrows, and Connecticut warblers .
Moose: Bog birch accounted for 11.8% of summer and 0.7% of winter moose forage on the Red Rock Lakes National Wildlife Refuge . It is preferred browse in Banff and Jasper National Parks, Alberta , but is not preferred by moose in Alaska .
Caribou: Buds, leaves, and sprouts of bog birch are preferred foods for caribou in Alaska in the spring and early summer. The rumens of 6 caribou examined in mid-June contained almost exclusively bog birch. Caribou eat the leaves extensively into June and July, but by mid-September the leaves are less palatable than willow (Salix spp.) leaves [135,159]. Caribou also eat bog birch in summer and winter in northern Canada [20,36,72,128]. Heavy browsing by the RiviÃ¨re George caribou herd in northern Quebec depleted winter carbohydrate reserves in bog birch, leading to decreased bog birch growth in spring .
Birds: Several species of ptarmigan and grouse eat bog birch in Alaska, Canada, and the contiguous northern United States [107,159]. Sharp-tailed grouse and greater prairie-chickens eat bog birch buds in Wisconsin in the winter , and spruce grouse eat bog birch seeds in central Alaska . Bog birch and dwarf birch buds and catkins comprised 11% of the food in rock ptarmigan crops in Alaska in spring, 12% in summer, 45% in fall, and 79% in winter. For willow ptarmigan the 2 birches comprised 0% of food in crops in spring, 3% in summer, 4% in fall, and 12% in winter .
Small mammals: American beavers eat bog birch . Bog birch is a preferred winter food of snowshoe hares in the southwestern Yukon [39,88,122,136]. Eastern heather voles eat bog birch bark in the winter in Canada . White spruce/bog birch communities in the Kluane Region, Yukon, provide habitat for a number of small mammals including deer mice, northern red-backed voles, meadow voles, and heather voles .
Fish: Bog birch provides overhanging shade and cover for fish along low-gradient streams in western Montana .
Insects: Insect herbivores can cause "moderate" damage to bog birch. During the 1976 to 1980 growing seasons, bog birch plants in northern Quebec lost 20% to 50% of leaf biomass to insects . In Alaska, the total number of herbivorous insects decreased with increases in latitude and altitude and distance from the white spruce forest zone. More detailed information on insects found on bog birch foliage is available .
Bog birch importance rankings for 9 ungulate species in British Columbia are provided below.
|Importance of bog birch in the diets of ungulates in British Columbia |
|Sitka black-tailed deer||low|
|Rocky Mountain elk||moderate|
Palatability/nutritional value: The palatability of bog birch in several states is as follows
|Palatability of bog birch for livestock and wildlife [28,38,46,67,125]:|
The energy and protein values of bog birch are low . Sugar content in bog birch leaves declines in late summer. Nitrogen concentration in leaves peaks early in spring then declines throughout the growing season . Nutritive values measured in bog birch plants near Inuvik, Northwest Territories, are given in the table below [129,130].
|Nutritive values in bog birch twigs and leaves [129,130]|
|Plant part||Month||Cu||Mo||Fe||Mn||Zn||K||Mg||Ca||P||crude fat||crude fiber||crude protein|
* No data available.
Bog birch produces carbon and nitrogen-based antiherbivore compounds that deter browsing . Sugar and nitrogen content is highest in the leaves in early spring. Bog birch allocates the greatest portion of its photosynthate to the production of antiherbivore phenolics at that time; otherwise, leaves would be susceptible to browsing insects .
Cover value: The table below summarizes thermal or feeding cover values of bog birch.
|Cover values of bog birch for wildlife in 3 western states [28,46]|
|upland game birds||good||fair||fair|
|small nongame birds||good||fair||good|
Bog birch provides cover for willow, rock, and white-tailed ptarmigan in southwestern Yukon . Grizzly bears in the central Canadian Arctic constructed their dens under bog birch cover more than any other plant species. Bog birch was present at 84% of 52 den sites, and it was the highest in percent cover around den entrances. Bog birch roots formed ceilings of several dens studied .
Betula glandulosa, American Dwarf Birch, also known as Resin Birch or Shrub Birch, is a species of birch native to North America, occurring in arctic and cool temperate areas from Alaska east to Newfoundland and southern Greenland, and south at high altitudes to northern California and Colorado in the west, and locally south to northern New York in the east. In the Arctic it occurs down to sea level, while in the south of the range, it grows as high as 3400 m altitude.
American Dwarf Birch is a multi-stemmed shrub typically growing to 1–3 m tall, often forming dense thickets. The trunks are slender, rarely over 5–10 cm diameter, with smooth, dark brown bark. The leaves are nearly circular to oval, 0.5–3 cm long and 1.2.5 cm broad, with a toothed margin. The fruiting catkins are erect, 1-2.5 cm long and 5–12 mm broad.
It is closely related to the Dwarf Birch (Betula nana), and is sometimes treated as a subspecies of it, as B. nana subsp. glandulosa. It is distinguished from typical B. nana by the presence of glandular warts on the shoots and longer leaf petioles. Hybrids with several other birches occur.
- Flora of North America: Betula glandulosa, RangeMap
- Hunt, D. (1993). Betula. Proceedings of the IDS Betula Symposium 2–4 October 1992. International Dendrology Society.
- USDA Plants Profile for Betula glandulosa (resin birch)
- Calflora Database: Betula glandulosa (Resin birch)
|This Fagales article is a stub. You can help Wikipedia by expanding it.|
Specimens of Betula glandulosa have been reported from the St. Lawrence Valley, but I have not seen them.
Wherever Betula glandulosa comes in contact with B . pumila , it forms a bewildering swarm of plants, known as B . × sargentii Dugle, having intermediate states of most vegetative characters.
Plants intermediate between Betula glandulosa and B . nana subsp. exilis make up a continuum of forms linking the typical forms of Betula nana and B . glandulosa in parts of Alaska where the ranges of these species overlap. Wherever they occur in isolation, the species remain reasonably distinct and easy to identify. In southern Greenland, Betula glandulosa hybridizes with B . nana subsp. nana and with B . pubescens .
Betula × eastwoodiae Sargent (= B . glandulosa × occidentalis ) occurs in montane meadows and marshes in Alberta, British Columbia, Northwest Territories, Saskatchewan, Yukon, Alaska, Colorado, and Wyoming, where the range of the parents overlap.
Betula × dugleana Lepage (= Betula glandulosa Michaux × B . neoalaskana Sargent) is common throughout Alaska and the Yukon, where the parent species frequently come into contact (E. Hultén 1941--1950, vol. 4; E. Lepage 1976).
Betula × dutillyi Lepage [= Betula glandulosa Michaux × B . minor (Tuckerman) Fernald] is a putative hybrid that occupies the same general range as Betula minor . Like that species, however, it has not been studied experimentally. Careful examination of the entire complex to which this taxon belongs will be necessary before any of its parts can be truly understood. Betula × dutillyi exhibits many of the same characteristics as B . minor , but it is slightly smaller in habit, and its leaves are smaller with somewhat blunter tips and more cuneate bases (E. Lepage 1976).
Names and Taxonomy
The scientific name of bog birch is Betula glandulosa
Michx. (Betulaceae) [31,54,60,61,75,76,77,137,159,168].
Bog birch hybridizes with dwarf birch (Betula nana subsp. exilis and
Betula nana subsp. nana) where
their ranges overlap [54,77,159]. Bog birch
also hybridizes with paper birch (Betula papyrifera) in interior Alaska .
Numerous other hybrids have been described including:
Betula ÃÂ sargentii Dugle (B. nana ÃÂ B. pumila)
Betula ÃÂ eastwoodiae Sargent (B. nana ÃÂ B. occidentalis) [31,51,54]
Betula ÃÂ dugleana Lepage (B. nana ÃÂ B. neoalaskana)
Betula ÃÂ dutillyi Lepage (B. nana ÃÂ B. minor, a
putative hybrid) 
EOL content is automatically assembled from many different content providers. As a result, from time to time you may find pages on EOL that are confusing.
To request an improvement, please leave a comment on the page. Thank you!