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Introductory

SPECIES: Vaccinium uliginosum | Bog Blueberry
ABBREVIATION : VACULI SYNONYMS : NO-ENTRY SCS PLANT CODE : VAUL COMMON NAMES : bog blueberry bog bilberry alpine blueberry alpine bilberry bog huckleberry bog whortleberry TAXONOMY : The currently accepted scientific name of bog blueberry is Vaccinium uliginosum Linnaeus [1,34,37,41,72]. It has been placed within the section Vaccinium of the taxonomically complex genus Vaccinium [81]. Recognized subspecies and varieties based on morphological characteristics or distribution are as follows: V. uliginosum ssp. alpinum (Bigel.) Hulten [37,87] V. uliginosum ssp. microphyllum Lange [37,41,81] V. uliginosum ssp. pubescens (Wormsk. ex Hornem.) Young [41,75,81] V. uliginosum ssp. occidentale (Gray) Hulten [41,81] V. uliginosum ssp. pedris (Harshberger) Young [41,81] V. uliginosum ssp. gaultherioides (Bigel.) Young [81] V. uliginosum var. alpinum Bigel. [23,37,72,75,87] V. uliginosum var. salicinum (Cham.) Hulten [37,81] V. uliginosum var. uliginosum Linnaeus [1,34,37,41,72] LIFE FORM : Shrub FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : Robin F. Matthews, April 1992 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Matthews, Robin F. 1992. Vaccinium uliginosum. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Vaccinium uliginosum | Bog Blueberry
GENERAL DISTRIBUTION : Bog blueberry is distributed throughout Alaska, Canada, and Greenland. It occurs south through New England, the northern portions of the Great Lakes States, and western Washington and Oregon [1,34,72,75,87]. Bog blueberry is also found in Japan, other parts of Asia, and in Europe [34,38,87]. ECOSYSTEMS : FRES10 White - red - jack pine FRES11 Spruce - fir FRES23 Fir - spruce FRES24 Hemlock - Sitka spruce FRES26 Lodgepole pine FRES44 Alpine STATES : AK CA ME MI MN NH NY OR VT WA WI AB BC LB MB NB NF NT NS ON PE PQ SK YT ADMINISTRATIVE UNITS : DENA GLBA ISRO LACL OLYM WRST YUCH BLM PHYSIOGRAPHIC REGIONS : 1 Northern Pacific Border 2 Cascade Mountains KUCHLER PLANT ASSOCIATIONS : K001 Spruce - cedar - hemlock forest K002 Cedar - hemlock - Douglas-fir forest K004 Fir - hemlock forest K008 Lodgepole pine - subalpine forest K015 Western spruce - fir forest K093 Great Lakes spruce - fir forest K094 Conifer bog K095 Great Lakes pine forest K096 Northeastern spruce - fir forest SAF COVER TYPES : 1 Jack pine 5 Balsam fir 12 Black spruce 13 Black spruce - tamarack 38 Tamarack 107 White spruce 201 White spruce 202 White spruce - paper birch 204 Black spruce 205 Mountain hemlock 206 Engelmann spruce - subalpine fir 218 Lodgepole pine 224 Western hemlock 225 Western hemlock - Sitka spruce 227 Western redcedar - western hemlock 228 Western redcedar 251 White spruce - aspen 253 Black spruce - white spruce 254 Black spruce - paper birch SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Bog blueberry can occur as a dominant or codominant in a variety of habitats within its range. It may occur as an understory component in open or closed forest habitats, primarily with black or white spruce (Picea mariana; P. glauca) [25,65,76,85,70]. Bog blueberry can also dominate or codominate in dwarf shrub types, bogs or muskegs, and on open tundra [27,43,86]. Other associated tree species include: Alaska-cedar (Chamaecyparis nootkatensis), quaking aspen (Populus tremuloides), balsam poplar (P. balsamifera), and paper birch (Betula papyrifera). Associated understory species include: willows (Salix spp.), alders (Alnus spp.), bog birch (Betula glandulosa), dwarf arctic birch (B. nana), Labrador tea (Ledum groenlandicum and L. palustre), lignonberry (Vaccinium vitis-idaea), bunchberry dogwood (Cornus canadensis), rustyleaf menziesia (Menziesia ferruginea), crowberry (Empetrum nigrum), red fruit bearberry (Arctostaphylos rubra), leatherleaf (Chamaedaphne calyculata), bog laurel (Kalmia polifolia), cloudberry (Rubus chamaemorus), bog rosemary (Andromeda polifolia), salal (Gaultheria shallon), fireweed (Epilobium angustifolium), Labrador lousewort (Pedicularis labradorica), entire leaf mountain avens (Dryas integrifolia), Mt. Washington mountain avens (D. octopetala), bluejoint reedgrass (Calamagrostis canadensis), altai fescue (Festuca altaica), cottonsedge (Eriophorum vaginatum and E. angustifolium), and various sedges (Carex spp.), feathermosses (Hylocomium, Pleurozium, and Stereocaulon spp.), clubmosses (Lycopodium spp.), sphagnum mosses (Sphagnum spp.), and lichens (Cladonia and Cladina spp.). Published classifications listing bog blueberry as a major component of plant associations (pas), community types (cts), or vegetation types (vts) are as follows: AREA CLASSIFICATION AUTHORITY interior AK postfire forest cts Foote 1983 nw AK cts Hanson 1953 AK gen. veg. pas Viereck & Dyrness 1980 AK: Seward Peninsula cts Kelso 1989 YT vts Stanek and others 1981 OR: Willamette NF gen. veg. pas Hemstrom and others 1987 Newfoundland peatland pas Pollett 1972 N.W.T. cts Black & Bliss 1978

VALUE AND USE

SPECIES: Vaccinium uliginosum | Bog Blueberry
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : Bog blueberry is consumed by many species of wildlife. Many songbirds and gamebirds including ptarmigan and spruce grouse eat the berries, often before they are ripe [57,80]. Bog blueberry leaves are important in the diet of spruce grouse throughout the spring, summer, and fall [20]. Many small mammals including chipmunks, squirrels, mice, and rabbits also consume bog blueberry leaves or fruits. Consumption of leaves by snowshoe hares is highest in the spring [91]. Ninety-two percent of the red-backed vole's fall diet consists of berries, many of which are bog blueberries [90]. Caribou and moose browse on bog blueberry. In northwestern Manitoba, occurrence of leaves and twigs in caribou rumen samples was 75 percent in April and 81 percent in November [61]. Bog blueberry was also detected in samples in the winter months but may have been consumed as litter as the caribou browsed on lichens [73]. Moose lightly browse bog blueberry throughout the year [52]. When available, bog blueberries are one of the most important fruits consumed by black bear in interior Alaska. The berries are utilized heavily from July to September [29]. Black bear browse on bog blueberry leaves in the spring [55]. Brown bear are also known to eat bog blueberries [60]. PALATABILITY : Palatability of Vaccinium species as browse is rated as fair to moderate [14]. NUTRITIONAL VALUE : The nutritional value of bog blueberry is not well documented. However, Vaccinium species in general have sweet berries that contain high concentrations of mono- and di-saccharides [77]. They are rich in vitamin C, high in energy content, and low in fat [68]. COVER VALUE : Bog blueberry presumably provides cover for a variety of small wildlife species. It often forms a dense understory layer that may serve as hiding or resting sites for birds or small mammals. VALUE FOR REHABILITATION OF DISTURBED SITES : Bog blueberry has been successful at naturally colonizing local seismic lines in the subarctic [44]. It has also naturally colonized borrow pits in tundra regions of northwestern Canada and may be of use in managed reclamation projects [45]. Bog blueberry is tolerant of high concentrations of heavy metals in the soil. Leaf tissues can accumulate uranium, copper, lead, zinc, nickel, and iron in large quantities with no apparent detrimental effects to the plant [15]. The ability to inhabit soils with high concentrations of these metals may favor the use of bog blueberry in certain revegetation programs. Bog blueberry could not be established from seed during the first growing season in simulated pipeline trenches near Fort Norman, Northwest Territories. Bog blueberry has, however, successfully germinated after one or two growing seasons when planted in other areas [59]. OTHER USES AND VALUES : Bog blueberries are edible and have good flavor [37]. The berries are often picked in large quantities [1,87] and used in jams, jellies, and pies [37,38]. They are the most popular fruit of Native Americans in the Fort Yukon region [35]. Fresh or dried leaves can be used for tea [71]. Blueberry (Vaccinium spp.) leaves, flowers, and rhizomes have been used for medicinal purposes [81]. Bog blueberry has no economic importance [8], but its cold hardiness (including late flowering) and resistance to the blueberry fungus Fusicoccum putrefaciens make it useful for hybridizing with more economically important species [33,81]. A high correlation exists between concentrations of uranium, copper, and lead in bog blueberry leaf tissues and levels of these metals in the surrounding soil. The ability of bog blueberry to reflect heavy metal concentrations in till favors its use as a tool in mineral exploration. The advantages and disadvantages of using bog blueberry for biogeochemical prospecting have been considered [15]. MANAGEMENT CONSIDERATIONS : Leaf production of bog blueberry increased in response to overgrazing by caribou in arctic Canada. Average cover was 9 percent in overgrazed areas but only 2 percent in areas that were not overgrazed [31]. In one study, bog blueberry showed no significant response to fertilization or irrigation [40]. White spruce stands on Willow Island, Alaska were subjected to clearcut and shelterwood treatments. Second year average percent cover and average percent frequency of bog blueberry in the stands were as follows [18]: Control Clearcut Shelterwood, 46 ft. Shelterwood, 30 ft. (14 m) spacing (9 m) spacing _____________________________________________________________ Cover 0.3 0.1 + 0.5 Frequency 6.0 7.0 3.0 13.0 Vegetative propagation of bog blueberry has been more successful with root or rhizome cuttings than with stem cuttings. Rooting percentages from both hardwood and softwood stem cuttings were poor, whereas 52 percent of rhizome cuttings produced shoots when planted immediately after collection [36]. Blueberries can also be grown from seed. In general, the seeds should be planted in a mixture of sand and peat. Seedlings grown in the greenhouse can be transplanted 6 to 7 weeks after emergence but should not be transferred to the field until after the first growing season. Blueberries are exacting in their site requirements and are difficult to establish on sites that do not meet their specific needs. Naturally occurring stands can usually be managed successfully [13].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Vaccinium uliginosum | Bog Blueberry
GENERAL BOTANICAL CHARACTERISTICS : Bog blueberry is a low, highly branched, deciduous shrub. It is prostrate to erect in form and generally reaches 8 to 16 inches (20-40 cm) in height. The leaves are oval and leathery, and twigs are slender. Older twigs have gray, shreddy bark. The flowers are white to pink and are borne singly or in clusters at the ends of stems. The fruit is a blue to black berry [1,75,87]. Bog blueberry can form dense mats or open extensive colonies [81]. Bog blueberry roots in the organic layer and is rhizomatous. Rhizome depth ranges from superficial to 6 to 8 inches (15-20 cm) below the surface [56]. Mycorrhizal associations exist on bog blueberry roots that allow for increased plant nitrogen levels [28,48,78]. Bog blueberry has a relatively high ratio of root biomass to shoot biomass [32,69]. These adaptations are important for nutrient uptake in the cold, poorly aerated, nitrogen-poor soils characteristic of bog blueberry sites [10,32]. RAUNKIAER LIFE FORM : Phanerophyte (Nanophanerophyte) Chamaephyte Cryptophyte (Geophyte) REGENERATION PROCESSES : Bog blueberry is capable of vegetative and sexual reproduction. It regenerates vegetatively by layering or sprouting from rhizomes. Seeds of most Vacciniums are not dormant and require no pretreatment for germination [13]. In one study, however, bog blueberry seeds exhibited shallow dormancy, and a 30-day cold stratification at 35 degrees Fahrenheit (2 deg C) increased germination success. Very few stratified or unstratified seeds germinated at temperatures below 59 degrees Fahrenheit (15 deg C) [7]. Seed viability of most Vacciniums is of short duration [85]. Seeds are readily dispersed by the birds and animals that eat bog blueberry fruits [63]. Bog blueberry seedlings can colonize exposed mineral soil [59], but seedlings are rare in established adult populations [21]. SITE CHARACTERISTICS : Bog blueberry occupies sites ranging from sea level to alpine zones [71]. It occurs in organic or inorganic soils that are generally acidic (pH 3.5 to 6.2) [81]. Bog blueberry can tolerate a wide range of soil moisture conditions and is found on well-drained to poorly drained sites. Bog blueberry is found in sites characteristic of cool-temperate to cool-mesothermal climates [47]. Bog blueberry occurs in a wide variety of habitats, such as coastal and interior bogs [2,6,49,51]; cottongrass tussock tundra [5,6]; low shrub tundra [2,5,9]; sedge meadows [6,39,46]; black or white spruce woodlands [2,5,81]; forested areas [71,87]; rocky or sandy shores of lakes and streams [8,11,42]; rock outcrops [12,72]; and barrens [23,72]. SUCCESSIONAL STATUS : Bog blueberry remains an important component of forest and woodland understory through the early, mid-seral, and late stages of succession [9,19]. It is important in the early shrub stages of tundra succession, as well as in climax stages [83]. Bog blueberry can also be found in dense, mature-climax forest stands [16,25]. Bog blueberry can sprout from underground plant parts following fire and remains important throughout successional stages. The following cover and frequency percentages were found in black spruce stands in interior Alaska [25]: Stage Years after fire Frequency(%) Cover(%) ___________________________________________________________________ Newly burned 0 - 1 38.0 less than 0.5 Moss-herb 1 - 5 62.0 3.0 Tall shrub-sapling 5 - 30 40.0 5.0 Dense tree 30 - 55 65.0 8.0 Mixed hardwood-spruce 55 - 90 59.0 5.0 Spruce 90 - 200+ 42.0 2.0 SEASONAL DEVELOPMENT : Bog blueberry flowers from June to early July. Fruits ripen from late July through September [23,42,75].

FIRE ECOLOGY

SPECIES: Vaccinium uliginosum | Bog Blueberry
FIRE ECOLOGY OR ADAPTATIONS : Bog blueberry sprouts from rhizomes or rootstocks following fire [53,64,82]. It roots in the organic layer and therefore only survives in patches where the organic layer is not consumed [9]. Fire destroys the seeds, so bog blueberry must invade burned areas from off-site sources [64]. Wildfires that occur in the wet sites that bog blueberry often occupies are generally low in severity. POSTFIRE REGENERATION STRATEGY : survivor species; on-site surviving root crown or caudex survivor species; on-site survivng rhizomes off-site colonizer; seed carried by animals or water; postfire yr 1&2

FIRE EFFECTS

SPECIES: Vaccinium uliginosum | Bog Blueberry
IMMEDIATE FIRE EFFECT ON PLANT : Fire generally top-kills bog blueberry. Moderate- to high-severity fires may also kill underground vegetative structures. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Bog blueberry sprouts from surviving rhizomes or rootstocks after low to moderate-severity fires. Burned aerial stems may also sprout [64,88]. Bog blueberry grows rapidly for the first 50 to 60 years after fire [9], and reaches its highest postfire cover and frequency 50 to 120 years after burning [4]. Bog blueberry leaves are larger in burned areas, even after 5 years [89]. Dyrness [17] found that bog blueberry in black spruce stands increased in biomass production after light summer fires. The increase in biomass production corresponded to an increase in nutrient uptake. Nutrient levels (percent dry weight) in lightly burned versus unburned areas were as follows: N P K Ca Mg ________________________________________________ unburned .613 .074 .192 .172 .056 lightly burned 1.85 .324 .966 .394 .130 In the 4 years following the Wickersham Dome Fire near Fairbanks, Alaska, bog blueberry in black spruce stands increased in percent cover and biomass production, but did not reach control levels. Recovery in lightly burned stands was much greater than in heavily burned stands [86]. Biomass production in bog blueberry decreased following a summer fire in tussock tundra near Fairbanks, Alaska. Production in burned areas was significantly lower (P<.05) than in adjacent unburned areas 13 years after the fire [24]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : Flower buds tend to be more numerous on new shoots, and periodic removal of old shoots may increase flower production in many species of Vaccinium [58]. Berry production, however, may be delayed for a few years. Ground fires of moderate severity favor growth and development of bog blueberry, and prescribed burning is the recommended management tool to increase berry yield [62]. Burning should take place in late fall or early spring before growth resumes [74]. In Russia, low- to moderate-severity ground fires caused 2.2 to 3.1 fold increases in the number of bog blueberry shoots per unit area. Annual growth increments also increased, and were nearly two times greater in plants on burned areas than in plants on unburned areas. Fruit production resumed 3 years after fire, and berries in burned areas were larger and healthier (more resistant to damage) than berries in other areas. Yield in burned areas was also greater than in adjacent unburned sites [62].

REFERENCES

SPECIES: Vaccinium uliginosum | Bog Blueberry
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Cambridge; New York: Cambridge University Press: 1-32. [13877] 6. Calmes, Mary A. 1976. Vegetation pattern of bottomland bogs in the Fairbanks area, Alaska. Fairbanks, AK: University of Alaska. 104 p. Thesis. [14785] 7. Calmes, Mary A.; Zasada, John C. 1982. Some reproductive traits of four shrub species in the black spruce forest type of Alaska. Canadian Field-Naturalist. 96(1): 35-40. [6361] 8. Chandler, F. B.; Hyland, Fay. 1941. Botanical and economic distribution of Vaccinium L. in Maine. Proceedings of the American Society for Horticultural Science. 38: 430-433. [9665] 9. Chapin, F. Stuart, III; Van Cleve, Keith. 1981. Plant nutrient absorption and retention under differing fire regimes. 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: 301-321. 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[13625] 36. Holloway, Patricia; Zasada, John. 1979. Vegetative propagation of 11 common Alaska woody plants. Res. Note PNW-334. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Forest and Range Experiment Station. 12 p. [1183] 37. Hulten, Eric. 1968. Flora of Alaska and neighboring territories. Stanford, CA: Stanford University Press. 1008 p. [13403] 38. Iwagaki, H.; Ishikawa, S.; Tamada, T.; Koike, H. 1977. The present status of blueberry work and wild Vaccinium species in Japan. Acta Horticulturae. 61: 331-334. [9701] 39. Juday, Glenn Patrick. 1988. Alaska research natural area: 1. Mount Prindle. Gen. Tech. Rep. PNW-GTR-224. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station. 34 p. [7875] 40. Karlsson, P. Staffan. 1985. Effects of water and mineral nutrient supply on a deciduous and an evergreen dwarf shrub: Vaccinium uliginosum L. and V. vitis-idaea L. Holarctic Ecology. 8: 1-8. [9157] 41. 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Related categories for Species: Vaccinium uliginosum | Bog Blueberry

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