John C. Zasada and Howard M. Phipps
Balsam poplar (Populus balsamifera) is the northernmost American hardwood. It grows transcontinentally on upland and flood plain sites but attains the best development on flood plains. It is a hardy, fast-growing tree which is generally short lived, with some trees reaching 200 years. Other names are balm-of-gilead, bam, tacamahac, cottonwood, or heartleaf balsam poplar. Many kinds of animals use the twigs for food. The light, soft wood is used for pulp and construction.
Regularity: Regularly occurring
Regularity: Regularly occurring
Global Range: Newfoundland, Labrador to northwest Alaska, northeastern British Columbia, east through Alberta, northern portions of the Great Lakes states, northern New England, and locally from Iowa to Connecticut and in the Rocky Mountains. (Fowells 1965)
-The native range of balsam poplar.
Comments: Climatic conditions vary throughout the ranges, but are often characterized by low seasonal temperature provided by high altitudes or northern latitudes, and short growing seasons. P. balsamifera most frequently grows in moist soils of various textures including subirrigated sandy and gravelly soils, calcareous clay loams, or silt loams. It grows at elevations from sea level to about 5,500 feet (1,676 m). It is usually found in cool lowlands such as alluvial bottoms, sandbars, stream banks, lake shores and swamps. It grows in pure stands or in the following forest types: aspen, balsam fir-paper birch, white spruce-balsam fir-paper birch, black ash-American elm-red maple, aspen-birch, white spruce-aspen, and black cottonwood-willow (Fowells 1965).
Habitat & Distribution
Known Pests: CRYPTORHYNCHUS LAPATHI
Xanthomonas populi infects and damages cracked, cream slime oozing shoot (one year old) of Populus candicans 'Aurora'
Other: major host/prey
fruitbody of Exidia thuretiana is saprobic on dead, fallen wood of Populus candicans
Other: minor host/prey
In Great Britain and/or Ireland:
Foodplant / spot causer
mostly hypophyllous, in small groups, rarely epiphyllous and singular uredium of Melampsora laricis-populina causes spots on live leaf of Populus candicans
Remarks: season: 7-10
immersed, in groups of 5 to 12 perithecium of Valsa sordida is saprobic on dead branch of Populus balsamifera
Remarks: season: 2-4
Associated Forest Cover
In eastern North America, balsam poplar is found mainly in mixed stands where other species dominate. In Saskatchewan, it is a component of the following forest types: Aspen-hazelnut (Populus tremuloides/Corylus cornuta), white spruce (Picea glauca)-feathermoss, aspen-sarsaparilla (Aralia nudicaulis)/twinflower (Linnaea borealis), white spruce/aspen-bunchberry (Cornus canadensis)/bishops cap (Mitella nuda), black spruce (Picea mariana)feathermoss, and white spruce-horsetail (Equisetum spp.) (31). Balsam poplar is uncommon in boreal white spruce forests east of about 75° longitude and is not present in black spruce stands east of 85 to 86° longitude. It grows with white spruce east of 75° longitude, however (45). Other associated trees are balsam fir (Abies balsamea), paper birch (Betula papyrifera), black ash (Fraxinus nigra), American elm (Ulmus americana), red maple (Acer rubrum), tamarack (Larix laricina), and northern white-cedar (Thuja canadensis).
In western and northern parts of the range, balsam poplar is associated with balsam/alpine fir (Abies lasiocarpa), aspen, paper birch, white spruce, and black spruce on upland sites. It reaches its most widespread development on the river flood plains. On these sites, it occurs in pure stands and is associated with mountain alder (Alnus incana) and various willows (e.g., Salix alaxensis, S. interior) during early stand development and white spruce in later stages when it finally disappears from these sites (53,57).
Low shrubs associated with balsam poplar include redosier dogwood (Cornus stolonifera), bunchberry, mountain maple (Acer spicatum), bearberry honeysuckle (Lonicera involucrata), beaked hazel, American cranberry bush (Viburnum trilobum), highbush cranberry (V edule), red raspberry (Rubus idaeus var. canadensis and strigosus), prickly rose (Rosa acicularis), mountain cranberry (Vaccinium vitis-idaea), devil's club (Oplopanax horridum), and red currant (Ribes triste).
Some associated herbaceous plants are horsetails (Equisetum arvense, E. pratense), bluejoint reedgrass (Calamagrostis canadensis), bedstraws (Galium boreale, G. triflorum), fireweed (Epilobium angustifolium), panicle bluebells (Mertensia paniculata), red baneberry (Actaea rubra), alpine pyrola (Pyrola asarifolia), claspleaf twistedstalk (Streptopus amplexifolius), wild sarsaparilla, butterbur (Petasites spp.), and bishops cap.
In mixed stands, various feathermosses (e.g., Hylocomium splendens, Pleurozium schreberi) and lichens may be associated with balsam poplar. In Alaska, two mosses, Eurhynchium pulchellum and Mnium cuspidatum, have been reported in flood plain stands (53). Moss and lichen cover is generally low in these stands.
Diseases and Parasites
Fire fuels differ in the various vegetation types where balsam poplar occurs. Pure stands of balsam poplar support fires of less intensity than those in mixed conifer-hardwood stands, and tree survival is greater. Early successional stands containing only hardwoods are less likely to burn intensely than later successional stages or mixed balsam poplar-conifer stands (41). Balsam poplar produces root suckers after fire, and burned sites can be colonized by seed reproduction when mineral soil seedbeds are created.
As rivers create sites for establishment of balsam poplar, they also destroy sites with established stands. This process can be gradual as the river slowly undermines its bank at the rate of a few feet per year, or the erosion can be dramatic. It is not uncommon to see river channels change by 30 to 60 m (100 to 200 ft) in several years. These channel changes can destroy significant areas of established poplar stands.
Moose, deer, elk, and other animals browse on balsam poplar stem material but eat little foliage (3). Stems as large as 5 cm (2 in) d.b.h. may be broken by moose and the tops browsed. Where browsing occurs for only 1 or 2 years, however, form is not adversely affected because subapical buds rapidly replace damaged terminals. Simulated browsing of 9 to 14-year-old poplars resulted in increased twig biomass, indicating that only under the severest, repeated browsing is it adversely affected (16).
Resin of balsam poplar appears to repel snowshoe hares, and foliar buds have higher resin contents than internodes. As a result, hares may eat internodes of twigs and stems but not the buds (3,38). High terpene and phenolic resin content are sufficient to reduce cellulose digestion, making balsam poplar less palatable to animals (43).
Girdling by hares or rodents can kill saplings or small trees above the girdle, but dormant buds from below the girdle usually form a new stem. Ruffed grouse may feed on staminate buds in the winter.
Beaver frequently cut balsam poplar growing along watercourses; usually, sprouts are not produced or, if they are, they either die or are browsed and subsequently die. On small streams, ponds created by beaver dams can kill poplars growing in or adjacent to ponded areas.
The poplar and willow wood borer (Cryptorhynchus lapathi), bronze poplar borer (Agrilus liargus), and the poplar borer (Saperda calcarata) are among the most damaging insects. They girdle or badly weaken trees larger than 2.5 cm (1 in) in diameter by tunneling in the main stem and limbs (9).
The forest tent caterpillar (Malacosoma disstria), satin moth (Sti1pnotia salicis), gray willow leaf beetle (Pyrrhalta decora decora), and aspen leaf beetle (Chrysomela crotchi) feed on balsam poplar foliage, but the species is not their principal host (1). The highly resinous buds and leaves of balsam poplar may render them relatively less palatable than the principal tree hosts (3).
In mature trees, the most common decay-causing fungal species is Phellinus tremulae with Pholiota destruens, Corticium expallens, and Bjerkandra adusta also being important. A canker caused by Neofabraea populi has been observed on balsam poplar in Ontario less than 3 cm (1.2 in) in diameter (22,23). The occurrence of decay varies with site conditions and among clones, with the latter appearing to be the most important cause of resistance (23). Infection by Rhytidiella moroformis causes a roughening of the normally smooth bark and the formation of deep furrows. Melampsora spp. cause a leaf rust and Linospora spp., a leaf blight (22). Venturia populina causes a leaf and twig blight and can stunt the main stem.
Septoria musiva and S. populicola cause a leaf spot and canker on balsam poplar seedlings. Septoria musiva was reported to cause the highest percentage of canker and leaf spot in southern Manitoba. Septoria incidence on native poplars within their range is negligible (61).
Frost damage occurs to trees of all ages in exposed stands established after bums and logging, in nursery stooling beds, and in plantations of hybrid poplar (60). Entire twigs may be shed. Distortion from frost damage occurs adjacent to cankers, and dieback results in burl formation, bud proliferation, sucker production, and uneven development of bark, leaf, and sapwood (60).
PESTS AND DISEASE: Populus spp. have many natural enemies. The poplar and willow borer, Cryptorhynchus lapathi, is the most serious insect pest of balsam poplar and causes considerable mortality of saplings (Fowells 1965). The forest tent caterpillar, Malacosoma disstria, will only feed on the foliage of P. balsamifera when other Populus spp. (P. tremuloides and P. grandidentata) found in the same area have been completely destroyed (Fowells 1965).
Moderate browsing by mammals such as deer causes little permanent damage to suckers. Mice, voles, and rabbits can girdle suckers, and beaver frequently cut larger trees.
Reaction to Competition
In primary succession on river flood plains, balsam poplar is an early invader and is associated with various willows and alder for about 20 years after formation (53). It appears to assume dominance as a result of greater stature and relative growth rate than willow and alder, which precede it in succession, and white spruce, which follows it (58,59). It may have an allelopathic effect on alder germination and germinant development, but these effects have not been substantiated under field conditions (27,58,59). Balsam poplar bud extracts inhibit nitrification under laboratory conditions, indicating the potential for nitrogen conservation within poplar stands and an effect on forest development and succession (49). It is the dominant species for about 50 years. White spruce gradually replaces balsam poplar, and by age 100 to 150 years, the poplar is a minor component of the stand. Deviations from this general pattern include the Yukon and Susitna Rivers where poplar stands more than 200 years old occur, and white spruce is a minor species present mainly in the understory.
Balsam poplar can be important in secondary succession on bums and cutovers or primary succession on lakeshores and sites severely disturbed by mining and construction. Asexual and sexual reproduction are important in burned and cutover areas, but only sexual reproduction is important on severely disturbed sites. Balsam poplar can reproduce asexually under stand conditions, but the suckers are short lived.
Expansion of the root system and subsequent sucker production can play an important role in clone development and colonization of a site after the seedling ortet becomes established. Extension of lateral roots 1 to 3 cm (0.4 to 1.2 in) in diameter has been observed to be at least 14 m (46 ft) in 15-year-old clones. Expansion of the root system ranged between 0.5 and 8.0 m (1.6 and 26 ft) in a 15-year-old clone; maximum rate of expansion occurred between 5 and 9 years (33). Root system expansion determined from clone size and age appears to be lower at treeline than at lower elevations where clones of about the same size occur but are 6 to 10 times older (6,33,35.).
On sites without active soil deposition, formation of the root system is predominantly downward and lateral. Depth of rooting is restricted on the relatively wet sites where balsam poplar is commonly found. Lateral root spread on upland sites is at least 8 to 12 in (26 to 39 ft).
Life History and Behavior
In Alaska, segments of stems and branches broken and buried during autumn logging contribute to regeneration. This buried material was from 2 to 6 cm (0.8 to 2.4 in) in diameter and 10 to 200 cm (4 to 79 in) long (69).
Dormant hardwood stem cuttings, as old as 10 to 15 years and probably older, will produce roots and new shoots. Older cuttings frequently take longer to root than younger cuttings. The distal portion of the current year's growth may root more poorly than the basal part of the current growth and 2-year-old wood. In a rooting study conducted with material from Ontario, cuttings collected after December had a higher percentage of rooting, more roots per cutting, and a higher percentage of cuttings with bud activity than those collected before December. Age of the parent tree had no effect on number of roots produced or bud activity (8). Clonal differences are a major source of variation in rooting percentage and the number of primary roots produced by dormant cuttings (15). Rooting potential for hardwood cuttings ranges from 75 to 100 percent (8,24); rooting of softwood cuttings ranges from 23 to 63 percent, depending on treatment (24).
Unrooted stem sections have been used with varying success in regeneration of field sites. In one study in Alaska, survival after 3 years ranged from 15 to 82 percent. Highest survival was observed on gravel substrates, least on silt and sand soils. Third-year height was greatest on silt and sand-1.2 m (3.9 ft) (28). In a prescribed bum, survival after 5 years was generally low; microsites burned to mineral soil supported the best growth. Relatively deep organic layers, whether burned or unburned, provide a poor environment for the establishment of unrooted stem cuttings (65,66).
Stem cuttings (hardwood and softwood or greenwood cuttings) have been the major means of stand establishment for the short-rotation intensive culture of balsam poplar and hybrid poplars in Wisconsin, Ontario, and other areas (20). Hardwood cuttings are grown in clonal orchards, harvested, stored, and planted either rooted or unrooted. Clones that are difficult to root may survive better if they are regenerated from rooted cuttings. Greenwood cuttings provide a means of rapidly increasing the number of desirable clones, but they must be rooted before planting (20).
In the greenhouse, root cuttings of balsam poplar clones from Utah produced surface suckers from suppressed buds and end suckers from the cambium at the cut end (46). Root cuttings also produce new lateral roots from the same origins as suckers. Alaskan clones respond similarly (69).
Production of suckers after disturbance of the parent tree varies; the response is generally less than that of aspen which suckers prolifically. In Alaska, stocking after 3 years ranged from 4 to 61 percent; densities were 1 to 2 plants/m² (3 to 8/milacre) in harvested balsam poplar stands. Suckers made up about 80 percent of the stocking in the summer- and winter-logged areas but only 27 percent in a fall-harvested area. Production was on intact and broken roots within the upper 2 cm (0.8 in) of the surface soil. Average diameter of roots producing suckers was 1 cm (0.4 in) (69). In a 40- to 50-year-old stand on the Tanana River in interior Alaska, stocking was 83 percent and density 2 trees/m² (8/milacre) (25). In Saskatchewan, sucker regeneration was observed on dry, moist, and wet regimes. Stocking was 12 percent in the aspen-hazelnut type; 5 percent in the white spruce-aspen-bunchberry type; 5 percent in the white spruce/feathermoss type; and 7 percent in the aspen/sarsaparilla/twinflower type (31).
Density of suckers is greatest on sites where the organic layers are disturbed. Organic layers are effective insulators and may limit sprouting by controlling soil temperature, particularly in high latitude forests (69).
Production of suckers may be important in the invasion and establishment of balsam poplar on disturbed sites and in primary succession. Expansion has been observed on flood plains from established stands to areas that did not have poplar (40). Colonization by clonal expansion is believed to be more important on dry sites where the probability of seedling establishment is low (33). The area covered by individual clones on productive forest sites is not well documented; one 15-year-old clone consisted of 27 ramets and covered an area of 350 m² (3,700 ft²) (33).
The extent of clonal development is best documented at elevational and latitudinal treeline sites where seedling establishment is limited and development of stands through vegetative growth is the main means of colonization and maintenance of the species (6,35). Scattered groves of balsam poplar in the Brooks and Alaska Ranges of Alaska were found to be individual clones. Representative clones covered from 100 to 200 m² (1,060 to 2,110 ft²) and contained from 90 to 150 ramets. Clones with the oldest ramets (114 years old) were found on the Brooks Range sites. Ramets did not occur in areas with dense shrub cover (35).
New shoots also form on stumps from suppressed buds and adventitious buds developed from undifferentiated inner bark. Most originate in the inner bark at the top of the stump. Sprouting response varies with genotype and declines as tree age increases. It may be high (50 to 100/stump) initially, but production and survival of sprouts vary with season and logging method. The percentage of stumps with sprouts declines over a 2- to 5-year period (69).
Balsam poplar stump sprouts may be of little potential value in replacement of trees in mature stands after disturbance because of the fragile connection between sprout and stump. In intensively cultured stands grown on short rotations, coppicing is used to replace the new crop after harvest of the original stand established from stem cuttings. Individual cuttings may produce 10 to 20 sprouts I year after harvesting; 4 to 8 sprouts will survive after 2 years (20).
The growth potential of balsam poplar vegetative reproduction is greater than that of early seedling growth. Average height of balsam poplar was about 1 m (3.2 ft) after 3 years; height of dominants was 2.5 to 3.0 m (8.1 to 9.8 ft). The age of suckers at breast height (1.5 m or 4.9 ft) varies with site quality and the degree and type of disturbance (21,25).
The most detailed data available for growth of vegetative reproduction comes from stands of a P. balsamifera x tristis hybrid established from stem cuttings. After harvest of the original stands, coppice stands are managed for several rotations. Mean annual increment (stem plus branchwood) is 21 to 25 t/ha (9.5 to 11.0 tons/acre), depending on stand age and rotation length (11). Other studies with this hybrid have shown that 1- and 2-year-old coppice stands are taller and more productive than stands of similar age established from stem cuttings. Architecturally, the stands are different in that each individual in coppice stands has 10 to 20 stems at age 1 and 4 to 8 stems at age 2. Stands from stem cuttings usually contain one stem per individual at this age (20).
Internode length on young vegetative regeneration is usually greatest in the lower part of the annual shoot. Buds are longest in the central part of the shoot, and the terminal bud is equal to the largest nodal bud. First-order branches are smallest at the base of the previous year's growth and longest near the top. Angle of divergence of first-order branches is 30° to 40° (37).
Germination is epigeal and can occur after the seed has separated from the silky hair or in association with the hairs. Under ideal conditions, germination is rapid, and cotyledons can be expanded in 18 to 24 hours (33,64). The rate of germination declines below 15° to 20° C (59° to 68° F) (64). A conspicuous ring of fine hairs is formed at the root-hypocotyl junction. These hairs anchor the seedling to the substrate until the radicle provides a more substantial foothold. Moist mineral soil surfaces are the best seedbeds. Seeds germinate on moist organic seedbeds, but seedling survival is poor, and most seedlings die soon after germination (6,59,67).
Seedling development depends on photosynthesis soon after germination. After the first growing season, hypocotyl length varies from 2 to 5 mm (0.08 to 0.20 in) under Alaska conditions. Tricotyledonous seedlings do occur, but they are rare. Albinism can be as high as 5 percent in some seed lots in Alaska. Leaf production begins with the development of two leaves separated by 0 to 4 mm (0 to 0.16 in); the first leaf is I to 3 min (0.04 to 0.12 in) above the cotyledons. Subsequent leaf production and internode development vary by microsite and with seedling density, with maximum production of 11 leaves under field conditions in Alaska. The third and fourth internodes are the longest (25).
The height and dry weight of first-year seedlings are affected by density (25,39). Seedlings grown in a greenhouse from an Ontario seed source ranged from 5 to 32 cm (2 to 12.5 in) in height and 11 to 220 mg (0.17 to 3.4 gr) per plant as density decreased from about 59,000 to 323 seedlings/m² (39). Seedlings grown under normal environmental conditions in interior Alaska ranged from 2 to 6 cm (0.8 to 2.4 in) tall at sowing densities ranging from 73,400 to 1 seeds/m² (6,820 to 0.1/ft²). First-year shoot growth was proleptic with no branch formation unless the apex was damaged. Dry weight of leaves and stems ranged from 20 to 520 mg (0.3 to 8.0 gr) (25). Average root length varied from 9 to 13 cm (3.5 to 5.1 in).
On flood plain sites, height growth of planted seedlings in early successional stages was twice that in later stages. Growth appeared to be controlled by nitrogen availability in some stages of succession and a combination of light, water, and nutrient availability in other stages. In greenhouse studies, balsam poplar seedling biomass was greater on soils from alder stands than on those from earlier successional stages, suggesting that poplar benefits from nitrogen fixation. The growth of seedlings on early successional soils increased significantly when they were fertilized, but growth on alder soils was not affected by fertilization (58). Natural seedlings were found only in the early successional stages, and growth rate was similar in each of these stages.
Seed Production and Dissemination
Although most balsam poplar seeds die within several weeks of dispersal, some remain viable for 4 to 5 weeks. Duration of viability is dependent on temperature and moisture; cooler, drier conditions prolong viability. Viability can be maintained at 90 percent or greater for at least 3 years when seed is stored in airtight containers at -10° C (14° F) (4,63,65).
Flowering and Fruiting
The regional ratio of male to female clones was found to be 1:1 on treeline sites in northern Quebec. Female clones occurred on sites with a relatively milder climate or those that were more fertile and mesic; male clones were more common on inland sites with drier soil conditions. Most stands were made up of more than one clone; however, monoclonal stands usually contained a male clone, and polyclonal stands usually had only female clones. Stand density and area were greater in male than in female clones (6).
Flower clusters (catkins) are 5 to 9 cm (2 to 3.5 in) with many small flowers about 3 mm (0.12 in) long. Male flowers have 20 to 30 reddish stamens. Mature female catkins are 10 to 15 cm (4 to 6 in) long. Capsules are a lustrous green during development but turn dull green at time of dispersal. Male flowers are shed promptly and decay; female catkins are shed shortly after dispersal is completed but remain identifiable for the remainder of the summer (2,56).
Growth and Yield
The form or branching pattern of young trees is excurrent, with a clearly defined main bole and conical crown. In the 80- to 100-year-old age class, trees tend to have a more rounded crown, however, and the central stem gives rise to a more deliquescent or decurrent growth habit. On good sites the excurrent growth habit is present to at least 40 to 50 years. On poorer sites, the decurrent growth habit may occur earlier. The branching system is composed of long and short shoots; short shoots produce most of the leaves. Long shoots account for height growth and lateral branch extension.
Balsam poplar vegetative buds exhibit unconditional dormancy in the fall and early winter. A brief chilling period removes this dormancy, however, and by early February, buds are largely in a state of imposed dormancy with active growth commencing as soon as the temperature is high enough (14).
Specific gravity of balsam poplar wood ranges from 0.326 to 0.346 and differs among sites. Within individual trees, specific gravity varies from 0.318 to 0.429 and is greatest at the top of the tree. Fiber length ranges from 1.02 mm (0.04 in) at breast height to 0.78 mm (0.03 in) at a bole position of 75 percent of total height. Sapwood pH averages 5.40 and heartwood 8.12. No significant differences were found among male and female clones in pH or wood and bark extractives. Lignin content of wood was higher in the sapwood than in the heartwood; bark lignin content was three times greater than that of the wood (32,48).
Balsam poplar stands are generally even-aged, with some variation. On upland sites in Saskatchewan, the greatest age span is about 17 years, but most stands have an age range of 5 years or less (10). Age spans are 20 to 25 years or less in young stands and 50 to 60 years in 155- to 165-year-old stands occupying flood plain sites in northeast British Columbia (40).
The greatest age spans have been observed in the poplar groves characteristic of treeline stands. Clones in Alaska treeline stands have ramets ranging in age from I to more than 100 years old. New suckers tend to be produced at the periphery of the clone (35).
Stand density varies with stand history. The density of stems larger than 2.5 cm (1 in) varies from 8700/ha (3,250/acre) in 25-year-old stands to 225/ha (91/acre) in 200-year-old stands (53). In southern portions of the species' range, stand density is not well documented but is probably lower than in northern areas because balsam poplar does not normally occur in large pure stands. In Wisconsin, balsam poplar made up less than 2 percent of the total stand volume in the types where it was present (for example, balsam fir-white spruce, aspen, and tamarack) (12). In mixed-wood sections, balsam poplar makes up 7 percent of the total volume and annual growth (31), but this percentage varies with site type and drainage (table 1).
Table 1- Density and volume of balsam poplar in Saskatchewan by site type and drainage (adapted from 23) Site type and drainage Density Volume trees/ha trees/acre Pct of stand m²/ha ft²/acre Pct of stand Whitespruce- feathermoss,
well drained 17 7 3 11 157 5 White spruce/ aspen-bunchberry,
well drained 86 35 7 14 200 7 Aspen-hazelnut,
well drained 91 37 12 22 314 10 Jack pine-feather-moss/
club moss, moderately well drained 7 3 1 2 26 1 White spruce- feathermoss, moderately well drained 44 18 6 25 357 8
Total balsam poplar biomass estimates in Alaska range from 75 t/ha (33 tons/acre) in the Yukon River drainage to 180 t/ha (80 tons/acre) on the Tanana River flood plain for 60-year-old stands (29,68). In Alberta, aboveground dry weight for trees 16 to 65 years old varied from 0.45 to 251 kg (0.99 to 553 lb); 33 to 71 percent of this weight was in the main stem (30).
Forest survey reports for Alaska indicate that, in unmanaged stands, balsam poplar (or the hybrid with P trichocarpa) has a mean annual increment of from 4 to 6 m³/ha (57 to 86 ft³/acre) in the Susitna Valley. Site indices (base age 100 years) in British Columbia range from 6 to 12 ft (low) to 34 to 42 ft (good) (21).
Molecular Biology and Genetics
Balsam poplar and black cottonwood (Populus trichocarpa) have hybridized and produced mixed populations. Because of this intermixing, black cottonwood has been suggested as a subspecies (i.e., Populus balsamifera subsp. trichocarpa) (2,37). Where balsam poplar and black cottonwood overlap, hybrids with a range of characters intermediate to those of the two species are found. An index using capsule shape, capsule pubescence, and carpel number has been developed (2,55). Other hybrids have been reported between balsam poplar and P alba, P. laurifolia, P nigra, R simonii, P. sauveolens, P. tremula, and P tristis (7,37,69).
Barcode data: Populus balsamifera
Statistics of barcoding coverage: Populus balsamifera
Public Records: 14
Specimens with Barcodes: 23
Species With Barcodes: 1
National NatureServe Conservation Status
Rounded National Status Rank: N5 - Secure
Rounded National Status Rank: N5 - Secure
NatureServe Conservation Status
Rounded Global Status Rank: G5 - Secure
Global Short Term Trend: Increase of 10 to >25%
Comments: Aspen invasion of grasslands especially at the prairie-forest border has increased primarily because of fire suppression (Buell 1959, Maini 1960, Blake 1963). Aspen groves that were present in the prairie just prior to that time often were of small, brush-like trees instead of tall specimens. Increased wetland drainage probably also has encouraged aspen invasion (Buell 1960)
Undisturbed aspen clones expand into adjacent prairie when light, moisture and soil conditions are appropriate especially for vegetative growth (Maini 1966b). Vigorous root suckers emerge in the prairie at the periphery of a clone, where other woody plants also frequently invade the prairie. As these suckers grow, and crowns coalesce, aspen shades out desirable grassland species.
Rate of invasion is related to disturbance, clone phenotype, slope, wind, moisture, drainage, soil texture and climate.
Aspen persists in prairie regions because of its preference for full sun and its vigorous vegetative reproduction and clonal growth that is well-adapted to top removal (fire, cutting, browsing) and drought.
Relevance to Humans and Ecosystems
Balsam poplar hybrids have a potential for a variety of uses. Populus balsamifera x R deltoides (Populus x jackii) are used as windbreak and shelterwood plantings in the northern plains region. Other balsam poplar hybrids are being tested in short rotation, intensive culture plantations. When properly cultivated, irrigated, and fertilized, these hybrids yield about three or four times as much biomass as native aspen in northern Wisconsin. The resulting pulpwood is of acceptable quality. The foliage and small woody component can be converted to an animal feed supplement (26,70).
Balsam poplar and its hybrids are used or have potential value in urban forestry and soil stabilization projects, particularly in the northern portion of the range and in the plains area of western Canada where the number of indigenous species available for these purposes is limited. In urban situations, however, balsam poplar has several undesirable traits. The branches of older trees tend to be brittle, female trees produce large amounts of residue from the spent catkins, and relatively rapid root suckering can result in unwanted colonization of lawns, sidewalks, and roadways.
Anyone that has ever walked into a poplar stand in the spring at bud break is impressed with the fragrance in the air. This fragrance comes from the volatile compounds in the buds and other parts of the tree. These compounds have been identified and may have useful biological and esthetic properties (38). Various extracts from the winter buds of poplar were recognized by native peoples as having therapeutic value. For example, a salve or ointment (balm of Gilead) made by heating the winter buds in oil was used to relieve congestion (52). In recent years, the bark has been collected and carved into figures that are sold in gift shops.
Names and Taxonomy
Comments: As treated here (following Kartesz, 1994), includes as a subspecies the plants often called Populus trichocarpa, the black cottonwood. LEM 17May95.
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