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Introductory

SPECIES: Betula papyrifera | Paper Birch
ABBREVIATION : BETPAP SYNONYMS : Betula cordifolia Regel Betula neoalaskana Sarg. Betula neoalaskana var. kenaica (W. H. Evans) Boivin Betula alaskana Sarg. Betula papyrifera var. humilis (Reg.) Fern. & Raup SCS PLANT CODE : BEPA COMMON NAMES : paper birch white birch canoe birch silver birch TAXONOMY : The currently accepted scientific name of paper birch is Betula papyrifera Marsh. [38]. It is wide ranging and exhibits considerable ecotypic variation. Six intergrading geographical varieties are recognized [38,57]: var. papyrifera - typical paper birch var. cummutata (Regel) Fern. - western paper birch var. cordifolia (Regel) Fern. - mountain paper birch var. kenaica (W. H. Evans) Henry - Kenai birch var. neoalaskana (Sarg.) Raup - Alaska paper birch var. subcordata (Rydb.) Sarg. - northwestern paper birch Birch (Betula spp.) is a genetically plastic genus, often with morphological variation continuous between species [51]. Hybridization is common. Paper birch naturally hybridizes with almost every native species in the genus. Named hybrids include [38,51,57]: B. p. var. neoalaskana x B. glandulosa = B. X eastwoodiae Sarg. (Syn. = B. X dugleana Lepage) B. papyrifera x B. nana = B. X hornei Butler B. papyrifera x B. populifolia = B. X caerulea Blanchard B. papyrifera x B. occidentalis = B. X utahensis (Britt.) Dugle (Syn.= B. X piperi Britton) B. papyrifera x B. pumila var. glandulifera = B. X sandbergii Britt. Crosses with yellow birch (B. alleghaniensis), sweet birch (B. lenta), and river birch (B. nigra) have not been named. LIFE FORM : Tree FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Ronald Uchytil, September 1991 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Uchytil, Ronald J. 1991. Betula papyrifera. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Betula papyrifera | Paper Birch
GENERAL DISTRIBUTION : Paper birch has a transcontinental distribution across northern North America. It grows from Newfoundland and Labrador west along the northern limit of tree growth across Canada to northwestern Alaska, south to Washington, east and north in the mountains to western Montana and southwestern Alberta, east across the Prairie Provinces to Manitoba, and south and east through the Lake States to New England. Scattered outlying populations occur in the Great Plains of Montana and North Dakota, the Black Hills, the Appalachian Mountains from central New York to western North Carolina, and the Front Range of Colorado [57]. Paper birch is cultivated in Hawaii [79]. Detailed descriptions of the ranges of the six varieties are available [38,66]. ECOSYSTEMS : FRES10 White - red - jack pine FRES11 Spruce - fir FRES18 Maple - beech - birch FRES19 Aspen - birch FRES20 Douglas-fir FRES21 Ponderosa pine FRES22 Western white pine FRES23 Fir - spruce FRES24 Hemlock - Sitka spruce FRES25 Larch FRES28 Western hardwoods FRES38 Plains grasslands STATES : AK CO CT HI ID IL IN IA ME MA MI MN MT NE NH NJ NY NC ND OH OR PA RI SD VT VA WA WV WI WY AB BC LB MB NB NF NT NS ON PE PQ SK YT ADMINISTRATIVE UNITS : ACAD ALPO APIS CACO CODA DEWA DENA EFMO GLAC GRSM INDU ISRO LACL MORU NOCA PIRO SARA SHEN WRST YUCH BLM PHYSIOGRAPHIC REGIONS : 2 Cascade Mountains 8 Northern Rocky Mountains 11 Southern Rocky Mountains 14 Great Plains 15 Black Hills Uplift 16 Upper Missouri Basin and Broken Lands KUCHLER PLANT ASSOCIATIONS : K011 Western ponderosa forest K012 Douglas-fir forest K013 Cedar - hemlock - pine forest K014 Grand fir - Douglas-fir forest K015 Western spruce - fir forest K017 Black Hills pine forest K066 Wheatgrass - needlegrass K081 Oak savanna K093 Great Lakes spruce - fir forest K095 Great Lakes pine forest K096 Northeastern spruce - fir forest K098 Northern floodplain forest K102 Beech - maple forest K106 Northern hardwoods K107 Northern hardwoods - fir forest K108 Northern hardwoods - spruce forest SAF COVER TYPES : 1 Jack pine 5 Balsam fir 12 Black spruce 14 Northern pin oak 15 Red pine 16 Aspen 17 Pin cherry 18 Paper birch 19 Gray birch - red maple 20 White pine - northern red oak - red maple 21 Eastern white pine 22 White pine - hemlock 23 Eastern hemlock 24 Hemlock - yellow birch 25 Sugar maple - beech - yellow birch 27 Sugar maple 30 Red spruce - yellow birch 31 Red spruce - sugar maple - beech 32 Red spruce 33 Red spruce - balsam fir 35 Paper birch - red spruce - balsam fir 37 Northern white cedar 39 Black ash - American elm - red maple 55 Northern red oak 60 Beech - sugar maple 107 White spruce 108 Red maple 201 White spruce 202 White spruce - paper birch 203 Balsam poplar 204 Black spruce 206 Engelmann spruce - subalpine fir 210 Interior Douglas-fir 213 Grand fir 217 Aspen 222 Black cottonwood - willow 224 Western hemlock 228 Western redcedar 251 White spruce - aspen 252 Paper birch 253 Black spruce - white spruce 254 Black spruce - paper birch SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : In boreal spruce ecosystems, paper birch forms nearly pure, pioneer communities on disturbed sites. It is rare in late successional or climax forests and generally restricted to openings. It is a principal component of boreal mixedwoods in Canada because its pioneering habit is favored by the relatively frequent 50- to 125-year fire return interval [17]. Codominants in mixedwoods include trembling aspen (Populus tremuloides), black spruce (Picea mariana), white spruce (P. glauca), jack pine (Pinus banksiana), and balsam fir (Abies balsamifera). In the Northern Great Plains, paper birch forms climax woodland communities on moist, north- or east-facing slopes [23,28]. Published classifications listing paper birch as a dominant in community types (cts), habitat types (hts), plant associations (pas), or ecosystem associations (eas) are presented below: Area Classification Authority interior AK postfire cts Foote 1983 AK general veg. cts Viereck & Dyrness 1980 AK: Kenai Peninsula forest veg. cts Reynolds 1990 MN: Boundary Waters general veg. cts Ohmann & Ream 1971 Canoe Area e MT, ne WY, w ND, forest & woodland hts Hansen & others 1984 w SD: Missouri Plateau sw ND woodland hts Girard & others 1989 c NF forest veg. cts Damman 1964 PQ: Gaspe Peninsula forest veg. cts Zolaseski 1988 St. Lawrence Valley general veg. pas Dansereau 1959 BC: Prince Rupert Forest general veg. eas Haeussler & others 1984 Region, Interior Cedar- Hemlock Zone w-c Alberta forest eas Corns & Annas 1986

VALUE AND USE

SPECIES: Betula papyrifera | Paper Birch
WOOD PRODUCTS VALUE : Paper birch wood is used commercially for veneer, plywood, and pulpwood. It is easily worked and takes finishes and stains readily. Furniture, cabinets, and numerous specialty items are made from paper birch lumber. Tree chips are used for pulp and paper manufacture, reconstituted uses, and fuel. It is commonly used as fireplace and wood stove fuel [57,66]. IMPORTANCE TO LIVESTOCK AND WILDLIFE : Paper birch is an important moose browse throughout most of its range. Its nutritional quality is poor in the winter, but it is important to wintering moose because of its sheer abundance in young stands [57]. Peek [49] listed paper birch as one of the five most important browse species eaten by moose in the East. In some areas, paper birch leaves are important in moose summer diets [36]. Although considered a "secondary-choice food", paper birch is an important dietary component of white-tailed deer [33]. In Minnesota, white-tailed deer eat considerable amounts of paper birch leaves in the fall [32]. Snowshoe hares browse paper birch seedlings and saplings and porcupines feed on the inner bark of trees [57]. In Newfoundland, paper birch was a preferred hare browse [33]. Paper birch is also eaten by beaver [24]. Numerous birds and small mammals eat paper birch buds, catkins and seeds. Redpolls, siskins, and chickadees obtain a considerable portion of their annual diet from birch seeds [51,57]. Voles and shrews also eat the seeds [51]. Ruffed grouse eat paper birch catkins and buds [57]. Paper birch is a favorite feeding tree of yellow-bellied sapsuckers, which peck holes in the bark to feed on the sap [33]. Hummingbirds and red squirrels also feed at sapwells in paper birch created by sapsuckers [44]. PALATABILITY : Paper birch is a palatable moose browse. In Alaska moose prefer it over aspen, balsam poplar (Populus balsamifera), and alder (Alnus spp.) but prefer it less than willow (Salix spp.), which is the most palatable moose browe [57]. Shaw [59] reported that white-tailed deer in the Northeast exhibit a clear preference for birches. Beaver generally prefer aspen, while willow and paper birch are second choice foods [77]. NUTRITIONAL VALUE : Paper birch is a poor-quality winter moose browse. At this time of year, twigs provide adequate amounts of protein (about 7 to 8.5% [14,48]) but are not easily digested because of high levels of lignin [36,48]. Moose may die in the winter if restricted entirely to a diet of paper birch [36]. Paper birch leaves sampled in July contained 16.9 percent protein [48]. COVER VALUE : Young paper birch stands provide prime deer and moose cover [57]. Numerous cavity-nesting birds nest in paper birch, including woodpeckers, chickadees, nuthatches, and swallows [44,56]. VALUE FOR REHABILITATION OF DISTURBED SITES : Paper birch is useful for long-term revegetation and soil stabilization of severely disturbed sites. It is used to reclaim coal, lignite, rock phosphate, slate, gold, oil-shale, bauxite, and other mine spoils [52,70]. Best results are obtained by planting 2-year-old or older bare-root or containerized stock [52]. It is occasionally transplanted as wildlings. Methods for collecting, extracting, cleaning, storing, and sowing paper birch seed to produce nursery grown seedlings are available [11,26,70]. Paper birch may also be propagated by grafting, air layering, rooting of cuttings, or tissue-culture techniques [57]. OTHER USES AND VALUES : Paper birch's graceful form and attractive bark make it a popular landscape plant [57]. The sap is made into syrup, wine, beer, and medicinal tonics. Currently only a few small sugaring operations in Alaska utilize paper birch [57]. Native Americans made paper birch bark into baskets, storage containers, mats, baby carriers, moose and bird calls, torches, household utensils, and canoes [30]. The strong and flexible wood was made into spears, bows, arrows, snowshoes, sleds, and other items [30]. MANAGEMENT CONSIDERATIONS : Silviculture: Paper birch is shade-intolerant and can regenerate under even-aged silviculture. Clearcutting is the most common silvicultural system used for paper birch, but shelterwood, strip cuts, and small patch cuts are used to provide partial shade where summer precipitation is limiting [58]. For good seedling establishment at least 50 percent of the cut area should be scarified [58]. Wildlife damage: Severe deer or moose browsing in clearcuts can prevent or delay paper birch regeneration [6,33]. Following timber harvest in Newfoundland, paper birch regeneration averaged 13 inches (33 cm) tall where moose densities were high but averaged nearly 50 inches (127 cm) elsewhere [6]. Snowshoe hare and other small mammals often clip or gnaw the bark of planted seedlings [57]. Chemical control: Paper birch is susceptible to 2,4-D, 2,4,5,-T, dichlorprop, or glyphosate applied as a foliar spray [10,24]. Glyphosate, hexazinone, or triclopyr applied by hypohatchet also kill paper birch [24]. Leaf litter/conifer germination: Paper birch leaf litter inhibits jack pine, red pine (Pinus resinosa), and eastern white pine (P. strobus) seed germination [51]. Insects: The bronze birch borer is the most serious insect pest of paper birch. It attacks and can kill injured, overmature, or decadent trees [12]. There are numerous defoliators of paper birch, but they seldom cause mortality of healthy trees [57]. Diseases: Bacteria or decay fungi enter paper birch boles through wounds and branch stubs, and roots which come in contact with the roots of other trees infected with rootd- rotting fungi [57,60]. Trees in Alaska are very susceptible to decay, but elsewhere tend to contain little defect [76]. Most diseases can be identified by observing external signs [60].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Betula papyrifera | Paper Birch
GENERAL BOTANICAL CHARACTERISTICS : Paper birch is a medium-sized, single- or multiple-stemmed, deciduous tree. In forests it typically has a slender trunk with a narrow crown, but in openings it has a wider crown spreading out from near the base [24]. Multiple-stemmed trees are relatively common as a result of browsing by moose and snowhoe hares [21]. Throughout much of its range, mature trees are 70 to 80 feet (21-24 m) tall and 10 to 12 inches (25-30 cm) in trunk diameter, but sometimes grow up to 30 inches (75 cm) in diameter [31,57]. In Alaska, paper birch trees are commonly 20 to 60 feet (6-18 m) high and 4 to 12 inches (10-30 cm) in trunk diameter [66]. Paper birch is short-lived. Height growth ceases at about 60 to 70 years of age; few trees live more than 140 years [24]. Paper birch is shallow-rooted with few roots found deeper than 24 inches (60 cm) below the soil surface [57]. The bark is reddish-brown on saplings. On mature trees bark is thin, white, and smooth, often separating into papery strips, and is easily peeled off in sheets [24,66]. Male and female flowers occur in separate, pendulous catkins on the same tree [24]. Fruits are winged-nutlets 0.06 inch (1.5 mm) long by 0.03 inch (0.8 mm) wide [57]. RAUNKIAER LIFE FORM : Undisturbed State: Phanerophyte (mesophanerophyte) Burned or Clipped State: Chamaephyte Burned or Clipped State: Hemicryptophyte Burned or Clipped State: Therophyte REGENERATION PROCESSES : Seed production: Paper birch is a prolific seed producer. Seed production begins at about age 15, with optimum production at 40 to 70 years of age [11]. Trees produce good seed crops about every other year. Seed production over a 3-year period in Maine ranged from 2.4 to 9.8 million seeds/acre (5.9-24.2/ha) in a paper birch stand with 149 seed trees per acre (368/ha) [8]. In undisturbed paper birch stands in Alaska, seed production varied between 2.2 and 294 million seeds/acre (5.4-728 million/ha) [72]. Dispersal: The small, double-winged seeds are dispersed primarily by wind. Most seeds fall 100 to 200 feet (30-61 m) from the parent tree [43]. Seedfall at a clearcut edge was 60 percent of that within the uncut stand, and at 328 feet (100 m) into the cut seedfall was 10 percent of that within the stand [57]. Seed may travel great distances when blown across crusted snow [57]. Nearly all the seed (about 90 to 95 percent) is shed from September through November [51,57]. Seed quality and dormancy: Discolored and empty seeds make up 14 to 47 percent of a crop [57]. Seed viability is highest during heavy seed crop years and lowest during light seed crop years. In Maine, germination was 77 percent during a heavy seed year, but only 13 and 24 percent during 2 normal years [42]. Seeds dispersed early have lower germination rates than those dispersed lateer [8]. A small percentage of the seeds can remain viable on the forest floor for several years [51]. Germination and seedling establishment: Germination normally takes place in the spring following dispersal. Germination is generally best on disturbed mineral or mixed mineral-organic soil seedbeds [24,57]. The small seeds are sensitive to soil moisture and temperature. Thus shade usually favors germination and initial establishment by preventing seedbeds from drying out and reaching excessively high temperatures [43]. South or southwest aspects, excessively drained soils, insufficient rainfall, competing vegetation, and unshaded and undisturbed seedbeds deter establishment [51]. Seedlings will not grow on soils with a pH less than 5.0 [51]. Although germination and early survival are often best on mineral soils, seedling growth is best on humus seedbeds in moderate or full sunlight [42]. First year seedlings are about 2 to 5 inches (5-12 cm) tall [51]. Vegetative reproduction: Paper birch sprouts following cutting or fire. Sprouts typically arise from the stump base or root collar [74]. Prolific sprouting is common in young trees, with some individuals producing up to 100 sprouts [74]. Sprout growth is rapid, sometimes up to 24 inches (60 cm) in the first growing season [24]. Sprouting vigor decreases with age. Forty to fifty percent of 100- to 125-year-old trees produced stump sprouts within 1 year after cutting, while 80 to 90 percent of 40- to 50-year-old trees produced sprouts [74]. SITE CHARACTERISTICS : Paper birch grows in climates ranging from boreal to humid and tolerates wide variations in the amount and pattern of precipitation [24]. It grows at the northern limit of tree growth in arctic Canada and Alaska, in boreal spruce woodlands and forests, in montane and subalpine forests of the West, in wooded draws of the northern Great Plains, and in coniferous, deciduous, and, mixed forests of the Northeast and Lake States [18]. It is shade-intolerant, and abundant on burned-over and cut-over lands where it often forms pure stands [31]. It is restricted to openings in older forests. Paper birch is most abundant on rolling upland terrain and alluvial sites but grows on almost any soil and topographic situation, including rugged mountain slopes, open slopes, rock slides, muskegs, and borders of bogs and swamps [21,24,57]. In interior Alaska, paper birch tends to dominate cool, moist, north and east aspects, while aspen dominates warmer and drier, south and west aspects [57]. In the mountains of New England and New York, paper birch is one of the few hardwoods found near timberline [76]. In North Dakota, it is mostly restricted to moist draws on north-facing slopes [9]. Soils: Paper birch grows best on deep, well-drained to moderately well-drained, sandy or silty Spodosols, Inceptisols, and Entisols common on glacial deposits [24,57]. It grows on a wide range of soil textures from gravels to silts, and grows on organic bog and peat soils [24]. Associated trees: In addition to those species listed under Habitat Types and Plant Communities, common associates include bigtooth aspen (Populus grandidentata), pin cherry (Prunus pensylvanica), yellow birch, gray birch (Betula populifolia), sugar maple (Acer saccharum), red maple (A. rubrum), and white ash (Fraxinus americana) in the southern and eastern part of its range, and red spruce (Picea rubens) and jack pine in boreal regions [76]. Understory: Conifer seedlings and saplings are typical under mature paper birch stands. Associated shrubs include American green alder (Alnus crispa), beaked hazel (Corylus cornuta), raspberries and blackberries (Rubus spp.), common bearberry (Arctostaphylos uva-ursi), blueberries (Vaccinium spp.), Bebb willow (Salix bebbiana), Scouler willow (S. scouleriana), highbush cranberry (Viburnum edule), Labrador-tea (Ledum groenlandicum), elder (Sambucus spp.), gooseberry (Ribes spp.), and dwarf bush-honeysuckle (Diervilla lonicera) [20,57,66]. In Alaska, Canada reedgrass (Calamagrostis canadensis) is prominent in paper birch stands, but other grasslike plants, sedges (Carex spp.), and lichens are principally absent [39]. In Labrador, lush herbs create a nearly continuous ground layer under paper birch stands [20]. SUCCESSIONAL STATUS : Paper birch is a short-lived, shade-intolerant, pioneer species. It rapidly colonizes open disturbed sites created by wildfire, windthrow, or avalanche but lasts only one generation before it is replaced by shade-tolerant conifers or northern hardwoods. Paper birch seeds-in aggressively after wildfire, often forming large, essentially pure stands [19,21,39]. Depending on the recovery of other species following fire, paper birch may also occur in mixed postfire stands with spruces, aspen, and other hardwoods [15,27,39]. Seral paper birch stands resulting from wildfire in Alaska commonly have 3,000 to 6,000 trees per acre (7,470-14,820/ha) 20 years after establishment [39]. By 60 to 90 years, stands have thinned to 500 to 800 trees per acre (1,235-1,976/ha) [19,39]. Seedbeds under these paper birch stand are unfavorable for germination of birch seed, but spruce seedlings are common. By 120 to 150 years after fire, black or white spruce dominate [39,66]. In southeastern Labrador, paper birch seedling establishment begins promptly after fire and is restricted to the first 15 postfire years. At 40 to 50 years after fire conifer seedlings appear in the paper birch understory. At 75 to 100 years, paper birch stands begin to deteriorate and are eventually replaced by conifers unless another fire initiates paper birch establishment [21]. In boreal mixed woods, paper birch begin dying by 75 years after fire. At this time jack pine, black spruce, and white spruce begin to dominate or codominate. By 125 years most paper birch are dead [17]. In contrast to other boreal regions, paper birch persists in forests for more than 200 years in eastern Quebec. This is probably due to spruce budworm outbreaks which cause white spruce to decline after about 200 years [5]. In the East, paper birch is commonly replaced by northern hardwoods on well-drained mineral soils, and by spruces and balsam fir on shallow or poorly drained soils [58]. In Minnesota, paper birch is often replaced by communities dominated by shrubs, particularly beaked hazel [58]. SEASONAL DEVELOPMENT : Paper birch male catkins are partially formed in the fall, remain dormant in the winter, and expand to a length of about 4 inches (10 cm) before flowering in the spring [43]. Female catkins appear in the spring before the leaves are fully expanded. In the southern portion of its range flowering begins in April [24]. In Alaska flowering occurs in May and June [66]. Seed dispersal may begin as early as August, but most seed is dispersed from September throughout November [8]. Paper birch phenological events proceed as follows in northeastern Minnesota [2]: Phenological event Time bud burst April leafing out late April - early May flowering begins April pollen shed late April - May seedfall begins August leaf color change September leaf fall late September - October

FIRE ECOLOGY

SPECIES: Betula papyrifera | Paper Birch
FIRE ECOLOGY OR ADAPTATIONS : Adaptation to fire: Paper birch is well adapted to fire, recovering quickly by means of seedling establishment and vegetative regeneration [1,39,67]. Seedling establishment is the most significant method of postfire recovery. Paper birch is a prolific producer of lightweight seeds that are easily dispersed by wind and readily germinate on fire-prepared seedbeds. Young trees sprout from the root collar following top-kill, but sprouting ability decreases after about 40 to 60 years of age [51]. Fire regime: Throughout most of Alaska and Canada, paper birch is found in boreal spruce and mixedwood forest types that burn at 50 to 150 year intervals [17,29]. Fire behavior: As a forest type, paper birch stands are one of the least flammable. The canopy often has a high moisture content and the understory is lush [21]. Crown fires in coniferous stands often stop at the boundary of large paper birch stands or become slow-moving ground fires [21,64]. As a result of this fire behavior, some large paper birch trees often survive fire in pure stands, and thus become seed trees for postfire establishment [51]. During dry periods, paper birch stands will burn readily. POSTFIRE REGENERATION STRATEGY : survivor species; on-site surviving root crown or caudex off-site colonizer; seed carried by wind; postfire years 1 and 2

FIRE EFFECTS

SPECIES: Betula papyrifera | Paper Birch
IMMEDIATE FIRE EFFECT ON PLANT : Fire generally kills or top-kills most paper birch trees; the thin, flammable bark makes the bole highly susceptible to girdling even by light surface fires [17,21,31]. Although the bark of older trees is thicker, it is also more flammable once it begins to exfoliate [39]. Paper birch seeds on the ground are destroyed by fire. Summer fires do not necessarily consume the catkins, but immature seeds will not ripen on killed or top-killed trees [63]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : On the Chippewa National Forest in Minnesota, prescribed burning in mid-May in aspen slash top-killed all 4- to 15-inch-diameter (10-38 cm) paper birch trees. These sprouted within a few weeks of the fire, but sprout mortality over the next few years resulted in 11 percent of the original trees dead by postfire year 5 [49]. Low-intensity prescribed surface fires (mean flame length > 1 foot [0.3 m], mean rate of spread of 10.8 feet [3.3 m] per minute) in a 30-year-old mixed hardwood stand in central Wisconsin did not kill or top-kill any paper birch trees greater than 4 inches (10 cm) in trunk diameter. Most of the saplings less than 4 inches in trunk diameter, however, were top-killed [54]. On the Kenai Peninsula, Alaska, 22 percent of paper birch trees were unaffected, while 78 percent had dead or partially dead aerial crowns 2 years after a light surface fire [69]. Forty-two percent of top-killed trees produced sprouts. Prescribed burning in a northern Wisconsin bracken fern (Pteridium aquilinum)-grassland killed 31 percent of paper birch trees present. The rest were top-killed but later sprouted. Basal area was reduced by 90 percent [68]. PLANT RESPONSE TO FIRE : Paper birch rapidly revegetates burned areas. Sprouts, and seedlings if seed trees are nearby, appear within the first postfire year. Sprout production: Young paper birch trees up to about 50 years old sprout prolifically and vigorously after fire. Sprouts appear a few weeks to 2 months after spring or summer fires but not until the following spring after late fall fires [35,50,61]. They grow rapidly and are often 20 to 40 inches (50-100 cm) tall after one growing season [1,35]. In Minnesota, 5-year-old postfire paper birch sprouts averaged 10 feet (3 m) in height [50]. Following prescribed spring fires at 5-year intervals in Idaho, paper birch averaged 31 to 58 basal sprouts per plant after each fire [35]. Sprout mortality is high in the first 5 postfire years, leaving a few to several sprouts per clump [50]. Seedling establishment: Mineral soils exposed by fire provide excellent paper birch seedbeds, but charred or partially removed organic layers prevent establishment. In Alaska, germination and subsequent seedling survival of artifically sown paper birch seed was abundant, practically nil, and nil on severely, moderately, and lightly burned test plots, respectively [73]. Undamaged trees within a burn or trees in nearby unburned stands are necessary for postfire seedling establishment. Where there are abundant seed trees, paper birch can easily establish 10's of thousands of seedlings per acre after fire [19,39,69]. In northern Saskatchewan, undamaged paper birch trees released 1 and 0.4 million seeds per acre (2.48 & 1 million/ha) in the first and second fall, respectively, following an April wildfire [4]. Because seed dispersal occurs in the fall, seedling establishment does not begin until the second postfire year [46]. Seedling establishment is generally greatest from postfire years 2 to 5 [3,46]. In Labrador, paper birch established by seed dated to within 15 years of fire, with subsequent seedling establishment lacking [21]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : In white spruce forest types in interior Alaska, paper birch establishes thousands of seedlings and sprouts shortly after fire. Sampling fire-origin paper birch stands in Alaska, Lutz [39] observed an average of 8,000 seedlings and saplings per acre (19,760/ha) 1 year after fire. Four years afer fire, Foote [19] observed an average of 12,000 stems per acre (30,000/ha) of both seed and sprout origin that were 3 to 6 feet (1-2 m) tall. Between 26 and 45 years after the fire, these thinned to a few thousand per acre. Three years after a prescribed light surface fire in south-central Alaska, on a site stocked primarily with white spruce and paper birch, there were about 8,000 and 1,000 paper birch seedlings and sprouts, respectively, per acre (19,760 and 2,470/ha) [69]. Seedlings averaged 6 inches (15 cm) and sprouts 14 inches (35 cm) in height. FIRE MANAGEMENT CONSIDERATIONS : Prescribed fire can be used to prepare cut-over sites for paper birch seed regeneration. In Maine, prescribed burning following winter logging favored paper birch establishment more than other treatments did. Burning or disking following logging exposed mineral soils on more than 70 percent of the logged area, while logging alone during the summer or winter, resulted in only 5 percent mineral soil exposure. Fourteen seed trees per acre (35/ha) were left on each treatment site. Paper birch seedling establishment was as follows [78]: Treatment Posttreatment year 1 Posttreatment year 10 #/acre #/ha #/acre #/ha winter logging/disked 245,400 605,200 3,300 8,200 winter logging/burned 50,100 123,700 4,800 11,900 summer logging only 65,700 162,300 1,700 4,200 winter logging only 33,700 83,200 1,900 4,700 Prescribed fire can be used to enhance deer and moose winter habitat by killing late successional conifers and promoting early successional browse species such as paper birch [69]. It generally takes 3 to 5 years after fire for paper birch sprout and seedling growth to provide adequate browse for deer and moose [57]. Peak browse production is generally between 10 and 16 years after fire [57].

REFERENCES

SPECIES: Betula papyrifera | Paper Birch
REFERENCES : 1. A. D. Revill Associates. 1978. Ecological eff. of fire and its mgmt. in Canada's national parks: a synthesis of the literature. Vols 1&2. Lit. Rev. & Annot. Bibliography. Ottawa, ON: Parks Canada, National Parks Branch, Natural Resources Division. 345 p. [3416] 2. Ahlgren, C. E. 1957. Phenological observations of nineteen native tree species in northeastern Minnesota. Ecology. 38(4): 622-628. [74] 3. Ahlgren, Clifford E. 1959. Some effects of fire on forest reproduction in northeastern Minnesota. Journal of Forestry. 57: 194-200. [208] 4. Archibold, O. W. 1980. Seed imput into a postfire forest site in northern Saskatchewan. Canadian Journal of Forest Research. 10: 129-134. [4506] 5. Bergeron, Yves; Dubuc, Michelle. 1989. Succession in the southern part of the Canadian boreal forest. Vegetatio. 79: 51-63. [5042] 6. Bergerud, Arthur T.; Manuel, Frank. 1968. Moose damage to balsam fir-white birch forests in central Newfoundland. Journal of Wildlife Management. 32(4): 729-746. [14203] 7. Bernard, Stephen R.; Brown, Kenneth F. 1977. Distribution of mammals, reptiles, and amphibians by BLM physiographic regions and A.W. Kuchler's associations for the eleven western states. Tech. Note 301. Denver, CO: U.S. Department of the Interior, Bureau of Land Management. 169 p. [434] 8. Bjorkbom, John C. 1971. Production and germination of paper birch seed and its dispersal into a forest opening. Res. Pap. NE-209. Upper Darby, PA: U.S. Department of Agriculture, Forest Service, Northeastern Forest Experiment Station. 14 p. [10975] 9. Bjugstad, Ardell J.; Girard, Michele. 1984. Wooded draws in rangelands of the northern Great Plains. In: Henderson, F. R., ed. Guidelines for increasing wildlife on farms and ranches: With ideas for supplemental income sources for rural families. Manhattan, KS: Kansas State University, Cooperative Extension Service; Great Plains Agricultural Council, Wildlife Resources Committee: 27B-36B. [4239] 10. Bovey, Rodney W. 1977. Response of selected woody plants in the United States to herbicides. Agric. Handb. 493. Washington, DC: U.S. Department of Agriculture, Agricultural Research Service. 101 p. [8899] 11. Brinkman, Kenneth A. 1974. Betula L. birch. In: Schopmeyer, C. S., technical coordinator. Seeds of woody plants in the United States. Agric. Handb. 450. Washington, DC: U.S. Department of Agriculture, Forest Service: 252-257. [46] 12. Conklin, James G. 1969. Insect enemies of birch. In: The birch symposium: Proceedings; 1969 August 19-21; Durham, NH. Res. Pap. NE-146. Upper Darby, PA: U.S. Department of Agriculture, Forest Service, Northeastern Forest Experiment Station: 151-154. [15353] 13. Corns, I. G. W.; Annas, R. M. 1986. Field guide to forest ecosystems of west-central Alberta. Edmonton, AB: Canadian Forestry Service, Northern Forestry Centre. 251 p. [8998] 14. Cowan, I. McT.; Hoar, W. S.; Hatter, J. 1950. The effect of forest succession upon the quantity and upon the nutritive values of woody plants used by moose. Canadian Journal of Research. 28(5): 249-271. [12820] 15. Damman, A. W. H. 1964. Some forest types of central Newfoundland and their relation to environmental factors. Forest Science Monograph 8. Washington, DC: Society of American Foresters. 62 p. [14281] 16. Dansereau, Pierre. 1959. The principal plant associations of the Saint Lawrence Valley. No. 75. Montreal, Canada: Contrib. Inst. Bot. Univ. Montreal. 147 p. [8925] 17. Day, R. J.; Harvey, E. M. 1981. Forest dynamics in boreal mixedwood. In: Whitney, R. D.; McClain, K. M., compilers. Boreal mixedwood: Proceedings of a symposium; [Date of conference unknown]; [Location of conference unknown]. COJFRC Symp. Proc. O-P-9. Sault Ste. Marie, ON: Environment Canada, Canadian Forestry Service, Great Lakes Forestry Research Centre: 29-41. [14204] 18. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. 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Upper Darby, PA: U.S. Department of Agriculture, Forest Service, Northeastern Forest Experiment Station: 83-85. [15351] 27. Hansen, H. L.; Krefting, L. W.; Kurmis, V. 1973. The forest of Isle Royale in relation to fire history and wildlife. Tech. Bull. 294; Forestry Series 13. Minneapolis, MN: University of Minnesota, Agricultural Experiment Station. 44 p. [8120] 28. Hansen, Paul L.; Hoffman, George R.; Steinauer, Gerry A. 1984. Upland forest and woodland habitat types of the Missouri Plateau, Great Plains Province. In: Noble, Daniel L.; Winokur, Robert P., eds. Wooded draws: characteristics and values for the Northern Great Plains: Symposium proceedings; 1984 June 12-13; Rapid City, SD. Great Plains Agricultural Council Publ. No. 111. Rapid City, SD: South Dakota School of Mines and Technology, Biology Department: 15-26. [1078] 29. Heinselman, Miron L. 1981. Fire intensity and frequency as factors in the distribution and structure of northern ecosystems. In: Mooney, H. A.; Bonnicksen, T. M.; Christensen, N. L.; [and others], technical coordinators. Fire regimes and ecosystem properties: Proceedings of the conference; 1978 December 11-15; Honolulu, HI. Gen. Tech. Rep. WO-26. Washington, DC: U.S. Department of Agriculture, Forest Service: 7-57. [4390] 30. Holloway, Patricia S.; Alexander, Ginny. 1990. Ethnobotany of the Fort Yukon region, Alaska. Economic Botany. 44(2): 214-225. [13625] 31. Hosie, R. C. 1969. Native trees of Canada. 7th ed. Ottawa, ON: Canadian Forestry Service, Department of Fisheries and Forestry. 380 p. [3375] 32. Irwin, Larry L. 1985. Foods of moose, Alces alces, and white-tailed deer, Odocoileus virginianus, on a burn in boreal forest. Canadian Field-Naturalist. 99(2): 240-245. [4513] 33. Jordan, James S.; Rushmore, Francis M. 1969. Animal damage to birch. In: The birch symposium: Proceedings; 1969 August 19-21; Durham, NH. Res. Pap. NE-146. Upper Darby, PA: U.S. Department of Agriculture, Forest Service, Northeastern Forest Experiment Station: 155-163. [15354] 34. Kuchler, A. W. 1964. Manual to accompany the map of potential vegetation of the conterminous United States. Special Publication No. 36. New York: American Geographical Society. 77 p. [1384] 35. Leege, Thomas A. 1979. Effects of repeated prescribed burns on northern Idaho elk browse. Northwest Science. 53(2): 107-113. [5116] 36. LeResche, Robert E.; Davis, James L. 1973. Importance of nonbrowse foods to moose on the Kenai Peninsula, Alaska. Journal of Wildlife Management. 37(3): 279-287. [13123] 37. Linde, Arlyn F. 1969. Controlled burning. In: Techniques for wetland management. Res. Rep. 45. Madison, WI: University of Wisconsin, Department of Natural Resources: 90-101. [12116] 38. Little, Elbert L., Jr. 1979. Checklist of United States trees (native and naturalized). Agric. Handb. 541. Washington, DC: U.S. Department of Agriculture, Forest Service. 375 p. 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Marquis, David A.; Solomon, Dale S.; Bjorkbom, John C. 1969. A silvicultural guide for paper birch in the northeast. Res. Pap. NE-130. Upper Darby, PA: U.S. Department of Agriculture, Forest Service, Northeastern Forest Experiment Station. 47 p. [10977] 44. McClelland, B. Riley. 1980. Influences of harvesting and residue management on cavity-nesting birds. In: Environmental consequences of timber harvesting in Rocky Mountain coniferous forests: Symposium proceedings; 1979 September 11-13; Missoula, MT. Gen. Tech. Rep. INT-90. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 469-514. [10315] 45. Methven, I. R.; Van Wagner, C. E.; Stocks, B. J. 1975. The vegetation of four burned areas in northwestern Ontario. Inf. Rep. PS-X-60. Chalk River, ON: Canadian Forestry Service, Petawawa Forest Experiment Station. 10 p. [13114] 46. Ohmann, Lewis F.; Grigal, David F. 1981. Contrasting vegetation responses following two forest fires in northeastern Minnesota. American Midland Naturalist. 106(1): 54-64. [8285] 47. Ohmann, Lewis F.; Ream, Robert R. 1971. Wilderness ecology: virgin plant communities of the Boundary Waters Canoe Area. Res. Pap. NC-63. St. Paul, MN: U.S. Department of Agriculture, Forest Service, North Central Forest Experiment Station. 55 p. [9271] 48. Oldemeyer, J. L.; Franzmann, A. W.; Brundage, A. L.; [and others]. 1977. Browse quality and the Kenai moose population. Journal of Wildlife Management. 41(3): 533-542. [12805] 49. Peek, J. M. 1974. A review of moose food habits studies in North America. Le Naturaliste Canadien. 101: 195-215. [7420] 50. Perala, Donald A. 1974. Growth and survival of northern hardwood sprouts after burning. Res. Note NC-176. St. Paul, MN: U.S. Department of Agriculture, Forest Service, North Central Forest Experiment Station. 4 p. [7349] 51. Perala, Donald A.; Alm, Alvin A. 1990. Reproductive ecology of birch: a review. Forest Ecology and Management. 32: 1-38. [12210] 52. Perala, Donald A.; Alm, Alvin A. 1990. Regeneration silviculture of birch: a review. Forest Ecology and Management. 32: 37-77. [12211] 53. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 54. Reich, Peter B.; Abrams, Marc D.; Ellsworth, David S.; [and others]. 1990. Fire affects ecophysiology and community dynamics of central Wisconsin oak forest regeneration. Ecology. 71(6): 2179-2190. [13326] 55. Reynolds, Keith M. 1990. Preliminary classification of forest vegetation of the Kenai Penninsula, Alaska. Res. Pap. PNW-RP-424. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station. 67 p. [14581] 56. Runde, Douglas E.; Capen, David E. 1987. Characteristics of northern hardwood trees used by cavity-nesting birds. Journal of Wildlife Management. 51(1): 217-223. [13743] 57. Safford, L. O.; Bjorkbom, John C.; Zasada, John C. 1990. Betula papyrifera Marsh. paper birch. In: Burns, Russell M.; Honkala, Barbara H., technical coordinators. Silvics of North America. Vol. 2. Hardwoods. Agric. Handb. 654. Washington, DC: U.S. Department of Agriculture, Forest Service: 158-171. [13960] 58. Safford, L. O.; Jacobs, Rodney D. 1983. Paper birch. In: Burns, Russell M., tech. comp. Silvicultural systems for the major forest types of the United States. Agric. Handb. 445. Washington, DC: U.S. Department of Agriculture, Forest Service: 145-147. [15358] 59. Shaw, Samuel P. 1969. Management of birch for wildlife habitat. In: The birch symposium: Proceedings; 1969 August 19-21; Durham, NH. Res. Pap. NE-146. Upper Darby, PA: U.S. Department of Agriculture, Forest Service, Northeastern Forest Experiment Station: 181-183. [15355] 60. Shigo, Alex L. 1969. Diseases of birch. In: The birch symposium: Proceedings; 1969 August 19-21; Durham, NH. Res. Pap. NE-146. 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Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station. 278 p. [2431] 66. Viereck, Leslie A.; Little, Elbert L., Jr. 1972. Alaska trees and shrubs. Agric. Handb. 410. Washington, DC: U.S. Department of Agriculture, Forest Service. 265 p. [6884] 67. Viereck, Leslie A.; Schandelmeier, Linda A. 1980. Effects of fire in Alaska and adjacent Canada--a literature review. BLM-Alaska Tech. Rep. 6. Anchorage, AK: U.S. Department of the Interior, Bureau of Land Mangement, Alaska State Office. 124 p. [7075] 68. Vogl, R. J. 1964. The effects of fire on the vegetational composition of bracken-grassland. Wisconsin Academy of Sciences, Arts and Letters. 53: 67-82. [9142] 69. Walker, Robert. 1979. 1979 progress report on the Chugach moose-fire program. In: Hoefs, M.; Russell, D., eds. Wildlife and wildfire: Proceedings of workshop; 1979 November 27-28; Whitehorse, YT. Whitehorse, YT: Yukon Wildlife Branch: 66-122. [14075] 70. Watson, L. E.; Parker, R. W.; Polster, D. F. 1980. Manual of plant species suitablity for reclamation in Alberta. Vol. 2. Forbs, shrubs and trees. Edmonton, AB: Land Conservation and Reclamation Council. 537 p. [8855] 71. Wolff, Jerry O.; Zasada, John C. 1979. Moose habitat and forest succession on the Tanana river floodplain and Yukon-Tanana upland. In: Proceedings, North American Moose Conference and Workshop No 15; [Date of conference unknown]; Kenai, AK. [Place of publication unknown]. [Publisher unknown]. 213-244. [6860] 72. Zasada, John C.; Gregory, Robert A. 1972. Paper birch seed production in the Tanana Valley, Alaska. Res. Note PNW-177. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Forest and Range Experiment Station. 7 p. [15357] 73. Zasada, John C.; Norum, Rodney A.; Van Veldhuizen, Robert M.; Teutsch, Christian E. 1983. Artificial regeneration of trees and tall shrubs in experimentally burned upland black spruce/feather moss stands in Alaska. 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Related categories for Species: Betula papyrifera | Paper Birch

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