Picea glauca, the white spruce, is a species of spruce native to the northern temperate and boreal forests in Canada and United States, North America.
Picea glauca is native from central Alaska all through the east, across western and southern/central Canada to the Avalon Peninsula in Newfoundland, Quebec, Ontario and south to Montana, North Dakota, Minnesota, Wisconsin, Michigan, Upstate New York and Vermont, along with the mountainous and immediate coastal portions of New Hampshire and Maine, where temperatures are just barely cool and moist enough to support it. There is also an isolated population in the Black Hills of South Dakota and Wyoming.
The conifer cone are pendulous, slender, cylindrical, long and 1.5 cm wide when closed, opening to 2.5 cm broad. They have thin, flexible scales 15 mm long with a smoothly rounded margin. They are green or reddish, maturing to pale brown 4 to 8 months after pollination. The seeds are black, 2 to 3 mm long, with a slender, tan wing 5 to 8 mm long.
Common causes of empty seed are lack of pollination, abortion of the ovule, and insect damage.
The average weight per individual seed varies from 1.1 mg to 3.2 mg.Hellum, A.K. 1976. Grading seed by weight in white spruce. USDA, For. Serv., Tree Plant. Notes 27(1):16–17, 23–24. (Cited in Coates et al. 1994).
Each seed is clasped by a thin wing 2 to 4 times as long as the seed. Seed and wing are appressed to the cone scale. Embryo and Gametophyte are soft and translucent at first; later the endosperm becomes firm and milky white, while the embryo becomes cream-coloured or light yellow. At maturity, the testa darkens rapidly from light brown to dark brown or black.Crossley, D.I. 1953. Seed maturity in white spruce. Canada Dep. Resour. and Devel., For. Branch, For. Res. Div., Ottawa ON, Silv. Res. Note 104. 16 p. Mature seeds "snaps in two" when cut by a sharp knife on a firm surface.
White spruce cones reach their maximum size after 800 GDD. Cone moisture content decreases gradually after about 1000 GDD.Cram, W.H.; Worden, H.A. 1957. Maturity of white spruce cones and seed. For. Sci. 3:263–269.
Cone colour also can be used to help determine the degree of maturation, but cones may be red, pink or green.Teich, A.H. 1970. Genetic control of female flower colour and random mating in white spruce. Can. Dep. Fish. For., Can. For. Serv., Ottawa ON, Bi-mo. Res. Notes 26:2. Collection and storage dates and conditions influence germination requirements and early seedling growth.Zasada, J.C. 1973. Effect of cone storage method and collection date on Alaskan white spruce ( Picea glauca) seed quality. p. 1–10 (paper 19) in Proc. Seed Problems. IUFRO Symp. Seed Processing, Bergen, Norway. Working Party S2.01, Royal Coll. For., Bergen, Norway, Vol. 1. CoatesEdwards, I.K. 1977. Fertility of transplant fields at the Prince Albert Forest Nursery. Can. Dep. Fish. Environ., Can. For. Serv., Northern For. Res. Centre, Edmonton AB, Inf. Rep. NOR-X-189. 21 p.Winston, D.A.; Haddon, B.D. 1981. Effects of early cone collection and artificial ripening on white spruce and red pine germination. Can. J. For. Res. 11:817–826.
A bushel (35 L) of cones, which may contain 6,500 to 8,000 cones, yields of clean seed.USDA Forest Service. 1948. Woody-plant Seed Manual. USDA, For. Serv., Washington DC, Misc. Publ. 654. 416 p.
Seed dispersal begins after cone scales reflex with cone maturation in the late summer or early fall of the year of formation. Cones open at moisture contents of 45% to 70% and specific gravities of 0.6 to 0.8. Weather affects both the initiation and pattern of seed dispersal, but cone opening and the pattern of seed dispersal can vary among trees in the same stand. Even after dispersal has begun, cold, damp weather will cause cone scales to close; they will reopen during dry weather. Most seed falls early rather than late, but dispersal may continue through fall and winter and even into the next growing season.Zasada, J. 1986. Natural regeneration of trees and tall shrubs on forest sites in interior Alaska. p. 44–73 in Van Cleve, K.; Chapin, F.S.; Flanagan, P.W.; Viereck, L.A.; Dyrness, C.T. (Eds.). Forest Ecosystems in the Alaskan Taiga: a Synthesis of Structure and Function. Springer-Verlag New York NY.Rowe, J.S. 1953. Viable seed on white spruce trees in midsummer. Can. Dep. Northern Affairs and National Resources, For. Branch, For. Res. Div., Ottawa ON, Silv. Leafl. 99. 2 p. Seed dispersal occurs mainly in late summer or early fall.
White spruce seed is initially dispersed through the air by wind. Both the initiation and pattern of seed dispersal depend on the weather, but these can vary among trees in the same stand. Small amounts of white spruce seed are normally dispersed beyond 100 m from the seed source, but exceptionally seeds have been found more than 300–400 m from the nearest seed source.
The structure of the tracheids in the long lateral roots of white spruce varies with soil nitrogen availability.Krasowski, M.J.; Owens, J.N. 1999. Tracheids in white spruce seedling's long lateral roots in response to nitrogen availability. Plant and Soil 217(1/2):215–228.
Slow-growing trees in rigorous are also capable of great longevity. White spruce high on the shore of Urquhart Lake, Northwest Territories, were found to be more than 300 years old.Hare, F.K.; Ritchie, J. 1972. The boreal bioclimates. Geogr. Rev. 62:333–365.
White spruce bark is mostly less than 8 mm and not more than 9.5 mm thick.Hale, J.D. 1955. Thickness and density of bark. Pulp and Paper Mag. Canada, Dec.:3–7.Chang, Y.P. 1954. Bark structure of North American conifers. USDA, For. Serv., Tech. Bull. 1095. 86 p.
P. glauca has three different genomes; a nuclear genome, a mitochondrial genome, and a plastid (i.e. chloroplast) genome. The large (20 Gbp) nuclear genome of P. glauca (genotype WS77111) was published in 2015, and the organellar (plastid and mitochondrial) genomes (genotype PG29) were published in SD Jackman et al. 2015. The plastid genome of P. glauca (genotype WS77111) has also been published.
The two western varieties are distinguished by pubescent shoots. It may be related to extensive hybridisation and intergradation with the closely related Engelmann spruce found further south in the Rocky Mountains, which forms the nothospecies Picea × albertiana. White spruce also hybridises readily with the closely related Sitka spruce where they meet in southern Alaska and northwestern British Columbia; this hybrid is known as Picea × lutzii.
Southern outliers have been reported in southern Saskatchewan and the Cypress Hills of southwestern SaskatchewanScoggan, H.J. 1957. Flora of Manitoba. Can. Dep. Northern Affairs and National Resources, Nat. Museum Can., Ottawa ON, Bull. 140. 619 p. and southeastern Alberta, northwestern Montana, south-central Montana, in the Black Hills on the Wyoming–South Dakota boundary, on the Manitoba–North Dakota boundary, and at Shushan, New York.Munns, E.N. 1938. The distribution of important forest trees of the United States. USDA, For. Serv., Washington DC, Misc. Publ. 287. 176 p.Fernald, M.L. 1950. Gray's Manual of Botany, 8th ed. Amer. Book, New York NY. 1632 p.Cook, D.B.; Smith, R.H. 1959. A white spruce outlier at Shushan, New York. Ecology 40:333–337.
White spruce is the northernmost tree species in North America, reaching just north of 69°N latitude in the Mackenzie River delta.Arno, S. F. & Hammerly, R. P. (1984). Timberline. Mountain and Arctic Forest Frontiers. The Mountaineers, Seattle. . It grows between sea level and an elevation of . Its northern distribution roughly correlates to the location of the tree line, which includes an isothermic value of for mean temperature in July, as well as the position of the Arctic front; cumulative summer degree days, mean net radiation, and the amount of light intensities also figure. White spruce is generally found in regions where the growing season exceeds 60 days annually.
The southern edge of the zone in which white spruce forms 60% or more of the total stand corresponds more or less to the July isotherm of around the Great Lakes; in the Prairie Provinces its limit is north of this isotherm. During the summer solstice, day length values range from 17 hours at its southern limits to 24 hours above the Arctic Circle.
One of the hardiest conifers, white spruce in parts of its range withstands mean daily January temperature of and extreme minimum temperatures as low as ; minimum temperatures of are general throughout much of the range except the southernmost and southeasternmost parts.Fowells, H.A. 1965. Picea (spruces). p. 287–327 in Silvics of Forest Trees of the United States. H.A. Fowells (Compiler), USDA, Forest Service, Washington DC, Agric. Handbook No. 271. By itself, or with black spruce and tamarack ( Larix laricina), white spruce forms the northern boundary of tree-form growth.Sutton, R.F. 1969. Silvics of white spruce ( Picea glauca Moench Voss). Can. Dep. Fish. For., For. Branch, Ottawa ON, Publ. 1250. 57 p. (Cited in Coates et al. 1994). White spruce up to 15 m in height occur at 69°N on islands in the Mackenzie Delta near Inuvik in the Northwest Territories. Hustich (1966)Hustich, I. 1966. On the forest–tundra and the northern tree-lines. Annales Univ. Turku A.II, Vol. 36:7–47. depicted Picea spp. as forming the northernmost limit of tree growth in North America.
The arctic or northern timberline in North America forms a broad transition zone from Labrador to northern Alaska. In Labrador, white spruce is not abundant and constitutes less than 5% of the forest, with a range that coincides very closely with that of black spruce but extending slightly further north.Wilton, R.F. 1964. The forests of Labrador. Can. Dep. For., For. Res. Branch, Ottawa ON, Publ. 1066. 72 p.
The range of white spruce extends westwards from Newfoundland and Labrador, and along the northern limit of trees to Hudson Bay, Northwest Territories, Yukon, and into northwestern Alaska. Across western Canada and Alaska, white spruce occurs further north than black spruce, and, while Populus ( Populus), willow, and birch may occur along streams well into the tundra beyond the limits of spruce, the hardwoods are usually no more than scrub.Hustich, I. 1953. The boreal limits of conifers. Arctic 6:149–162. Spruce characteristically occurs in fingers of tree-form forest, extending far down the northern rivers and as scattered clumps of dwarfed "bush" spruce on intervening lands.Halliday, W.E.D.; Brown, A.W.A. 1943. The distribution of some important forest trees in Canada. Ecology 24:353–373. In Manitoba, Scoggan noted that the northernmost collection of white spruce was at latitude 59°48'N, but Bryson et al.Bryson, R.A.; Irving, W.H.; Larson, J.A. 1965. Radiocarbon and soil evidence of former forest in the southern Canadian tundra. Science 147(3653):46–48. found white spruce in the northern edge of continuous forest in central Canada at Ennadai Lake, about 60°45′ N, 101°'W, just north of the northwest corner of Manitoba. Bryson et al. noted that the forest retained "the same general characteristics as when it was first described by in 1896". Collins and Sumner reported finding white spruce within 13 km of the Arctic coast in the Firth valley, Yukon, at about 69°30′ N, 139°30′ W, and Sargent noted that white spruce in Alaska "reached Behring Strait in 66°44′ N".
Climate, especially temperature, is obviously a factor in determining distributions of northern flora. Halliday and Brown suggested that white spruce's northern limit corresponds "very closely" with the July mean monthly isotherm of 10 °C in Ungava, but that the northern limit west of Hudson Bay was south of that isotherm. Other climatic factors that have been suggested as affecting the northern limit of white spruce include: cumulative summer degree days, position of the Arctic front in July, mean net radiation especially during the growing season, and low light intensities. Topography, soil conditions, and glaciation may also be important in controlling northern limits of spruce.Drew, J.V.; Shanks, R.E. 1965. Landscape relationships of soils and vegetation in the forest–tundra ecotone, Upper Firth River Valley, Alaska–Canada. Ecol. Monogr. 35:285–306.
The southern limit of distribution of white spruce is more complex. From east of the main range of coastal mountains in British Columbia, the southern continuous limit of white spruce is the forest/prairie interface through Alberta, Saskatchewan, Manitoba, the northern parts of Minnesota and Wisconsin, central Michigan, northeastern New York, and Maine. Sargent and Harlow and Harrar also included Vermont and New Hampshire; and, while Dame and BrooksDame, L.L.; Brooks, H. 1901. Handbook of the Trees of New England. Ginn, Boston MA. 196 p. excluded New York and states further west, they included Massachusetts as far south as Amherst and Northampton, "probably the southern limit of the species" in that area. NisbetNisbet, J. 1905. The Forester. Blackwood and Sons, Edinburgh and London, U.K., Vol. 1. 506 p. gave the range of white spruce as extending to "Carolina", but he did not recognize red spruce as a species and presumably included it with white spruce.
Towards the southern parts of its range, white spruce encounters increasingly effective ecological competition from , some of which may reinforce their growth-rate or sprouting competitiveness with allelopathic depredation of coniferous regeneration.Tubbs, C.H. 1976. Effect of sugar maple root exudate on seedlings of northern conifer species. USDA, For. Serv., Res. Note NC-213. 2 p. Further southward extension of the distribution is inhibited by white spruce's cold requirement.
Nisbet noted that firmly-rooted white spruce served very well to stabilize windswept edges of woods in Germany. In a narrow belt of mixed Norway and white spruces over an extremely exposed hilltop crest at high elevation in northern England, the Norway spruce were "completely dwarfed" whereas the white spruce had reached heights of between 3 and 4.3 m.Guillebaud, W.H.; Steven, H.M.; Marsden, R.E. 1920. Rate of growth of conifers in the British Isles. Forestry Commission, HMSO, London, U.K., Bull. 3. 84 p. The age of the belt was not recorded, but adjoining 66-year-old stands may have been of the same vintage.
White spruce has also been used as a minor plantation species in England and Scotland.Selby, P.J. 1842. A history of British forest-trees. Van Voorst, London. 540 p.Anon. (C.P.J.) 1879. Fir. pp. 222–225 in vol IX. Encyclopædia Britannica, 9th ed.United Kingdom Forestry Commission. 1920. Beaufort estate. p. 57–62 in Programme, British Empire For. Conf., London, U.K. In Scotland, at Corrour, Inverness-shire, Sir John Stirling Maxwell in 1907 began using white spruce in his pioneering plantations at high elevations on deep peat. However, plantations in Britain have generally been unsatisfactory,Edlin, H.L. 1962. A modern sylva or a discourse of forest trees. 3. The spruces. Quart J. For. 56:292–300. mainly because of damage by spring frosts after mild weather had induced flushing earlier in the season. However, the species is held in high regard in the Belgian peat region, where it grows better than other spruces.Fraser, G.K. 1933. Studies of certain Scottish Moorlands in relation to tree growth. For. Commission, HMSO, London, U.K. 112 p.
White spruce grows in soils with Soil pH values of 4.7–7.0, although they have been found in soils as acidic as 4.0 in Abies lasiocarpa forests in the Northwest Territories. A presence of calcium in the soil is common to white spruce found in northern New York. White spruce most commonly grows in the soil orders of Alfisols and Inceptisols. Soil properties such as fertility, temperature, and structural stability are partial determinants of the ability of white spruce to grow in the extreme northern latitudes. In the northern limits of its range, white spruce is the climax species along with black spruce; birch and aspen are the early succession species.
typically occur every 60 to 200 years, although they have been known to occur as infrequently as every 300 years.
White spruce will grow in Hardiness zone 3–7, but is not adapted to heat and humidity and will perform poorly in a hot climate. The tree attains its greatest longevity and growth potential in Zones 3–4.
Wildlife such as deer, rabbits, and grouse browse the foliage during the winter. The seeds are eaten by small mammals like the red squirrel and birds such as chickadee, nuthatch, and pine siskin.
Podzolized, brunisolic, luvisolic, gleysolic, and regosolic (immature) soils are typical of those supporting white spruce throughout the range of the species. Soils supporting white spruce are most commonly Alfisols or Inceptisols. In the podzol region of Wisconsin, white spruce occurs on loam podzols, podzolized gley loams, strongly podzolized clays, gley-podzol clays, stream-bottom soils, and wood peat. Moist sandy loams also support good growth. On sandy podzols, it is usually a minor species. Good development occurs on moist alluvium on the banks of streams and borders of swamps.Jeffrey, W.W. (1961). "Origin and structure of some white spruce stands on the lower Peace River." Can. Dep. For., For. Res. Branch, Ottawa ON, Tech. Note 103. 20 p.Jeffrey, W.W. (1964). "Forest types along lower Liard River, Northwest Territories." Can. Dep. For., For. Res. Branch, Ottawa ON, Publ. 1035. 103 p.Lacate, D.S.; Horton, K.W.; Blyth, A.W. (1965). "Forest conditions on the Lower Peace River." Can. Dep. For., For. Res. Branch, Ottawa ON, Publ. 1094. 53 p.Viereck, L.A. (1973). "Wildfire in the taiga of Alaska." Quaternary Res. 3:465–495.Sargent, C.S. 1898. The Silva of North America. A description of the trees which grow naturally in North America exclusive of Mexico. Vol. XII. Coniferae. Houghton Mifflin, Riverside Press, Cambridge, Boston MA. 144 p.Kenety, W.H. (1917). "Preliminary study of white spruce in Minnesota." Univ. Minnesota, Cloquet Exp. Sta. MN, Bull. 168. 30 p. White spruce makes good growth on well-drained lacustrine soils in Alberta Mixedwoods,Heger, L. (1971). "Site-index/soil relationships for white spruce in Alberta mixedwoods." Can. Dep. Environ., Can. For. Serv., For. Manage. Instit., Ottawa ON, Inf. Rep. FMR-X-32. 15 p. on moderately-well-drained clay loams in Saskatchewan,,Kabzems, A. (1971). "Growth and yield of well stocked white spruce in the mixedwood section , Saskatchewan. Saskatchewan." Dep. Nat. Resour., For. Branch, Prince Albert SK, Tech. Bull. 5. 75 p. (Cited in Coates et al. 1994). and on melanized loams and clays (with sparse litter and a dark-coloured organically-enriched mineral horizon) in the Algoma district of Ontario.
White spruce becomes less accommodating of soil with increasing severity of climate. The distribution of white spruce in Labrador seems to depend almost entirely on the character of the soil, and between the southwestern shores of Hudson Bay and the northeastern regions of Saskatchewan, white spruce is confined to very local physiographic features, characterized by well-drained or fertile soils.Ritchie, J.C. 1956. The vegetation of northern Manitoba. I. Studies in the southern spruce forest zone. Can. J. Bot. 34(4):523–561.
On dry, deep, outwash deposits in northern Ontario, both white spruce and aspen grow slowly.MacLean, D.W. (1960). "Some aspects of the aspen–birch–spruce–fir type in Ontario." Can. Dep. Northern Affairs National Resources, For. Branch, For. Res. Div., Ottawa ON, Tech. Note 94. 24 p. But, broadly, white spruce is able to tolerate considerable droughtiness of sites that are fertile, and no fertile site is too moist unless soil moisture is stagnant.Sutton, R.F. (1968). Ecology of young white spruce ( Picea glauca Moench Voss). Ph.D. thesis, Cornell Univ., Ithaca NY, Univ. Microfilms, Ann Arbor, Michigan MI, 68–11645. 500 p. Soil fertility holds the key not just to white spruce growth but to the distribution of the species. At least moderate fertility is needed for good growth, but white spruce occurs on many sites where nutrient deficiencies depress its growth more than that of black spruce, red spruce, Norway spruce, and the pines generally.Heiberg, S.O.; White, D.P. (1951). "Potassium deficiency of reforested pine and spruce stands in northern New York." Soil Sci. Soc. Amer. Proc. 15:369–376.
Forest floors under stands dominated by white spruce respond in ways that vary with site conditions, including the disturbance history of the site. Composition, biomass, and mineral soil physical and chemical properties are affected. In Alaska, the accumulation of organic layers (to greater thicknesses in mature stands of spruce than those in hardwood stands on similar sites) leads to decreased soil temperatures, in some cases leading to the development of permafrost.Viereck, L.A. (1970a). "Forest succession and soil development adjacent to the Chena River in interior Alaska." Arctic Alp. Res. 2(1):1–26. wS.Viereck, L.A. (1970b). Soil temperatures in river bottom stands in interior Alaska. p. 223–233 in Proc. Ecology of the Subarctic Regions, July–Aug. 1966, Helsinki, Finland, UNESCO. NienstaedtViereck, L.A.; Dyrness, C.T.; Van Cleve, K.; Foote, M.J. (1983). "Vegetation, soils, and forest productivity in selected forest types in interior Alaska." Can. J. For. Res. 13(5):703–720. Acidity of the mineral soil sampled at an average depth of 17 cm in 13 white spruce stands on abandoned farmland in Ontario increased by 1.2 pH units over a period of 46 years.Brand, D.G.; Kehoe, P.; Connors, M. (1986). "Pinophyta afforestation leads to soil acidification in central Ontario." Can. J. For. Res. 16(6):1389–1391.
A considerable range of soil pH is tolerated by white spruce. Thrifty stands of white spruce in Manitoba have developed on soils of pH 7.6 at only 10 cm below the surface, and pH 8.4 at 43 cm below the surface;Stoeckeler, J.H. (1938). "Soil adaptability of white spruce." J. For. 36:1145–1147.USDA Forest Service (1938). "White spruce on alkaline soils." USDA, For. Serv., Lake States For. Exp. Sta., St. Paul MN, Tech. Note 134. 1 p. rooting depth in those soils was at least 81 cm. An abundant calcium supply is common to most white spruce locations in New York state. Chlorosis was observed in young white spruce in heavily limed nursery soils at about pH 8.3. Wilde gave 4.7 to 6.5 as the approximate optimum range of pH for white spruce in Wisconsin, but optimum growth seems possible at pH levels up to 7.0 and perhaps higher. Alluvium on the floodplains of northern rivers shows pH levels from 5.0 to 8.2.Zasada, J.C.; Van Cleve, K.; Werner, R.A.; McQueen, J.A.; Nyland, E. (1977). "Forest biology and management in high-latitude North American forests." p. 137–195 in Proc. North American Forest Lands at Latitudes North of 60 degrees. Sympos., Univ. Alaska, Fairbanks AK, Sept. 19–22, 1977. High-lime ecotypes may exist,Pelletier, J.R. (1966). "Tree breeding in Canada." Commonw. For. Rev. 45(1):9–10. and in Canada Forest Section B8 the presence of balsam poplar and white spruce on some of the moulded moraines and clays seems to be correlated with the considerable lime content of these materials,Stiell, W.M. (1976). "White spruce: artificial regeneration in Canada." Dep. Environ., Can. For. Serv., Ottawa ON, Inf. Rep. FMR-X-85. 275 p. while calcareous soils are favourable sites for northern outliers of white spruce.
Mature stands of white spruce in boreal regions often have well-developed moss layers dominated by feather mosses, e.g., Hylocomium splendens, Pleurozium schreberi, Ptlium crista-castrensis, and Dicranum, rather than Sphagnum.La Roi, G.H.; Stringer, M.H. (1976). Ecological studies in the boreal spruce–fir forests of the North American taiga. II. Analysis of the bryophyte flora. Can. J. Bot. 54:619–643. NienstaedtViereck, E.G. (1987). Alaska's wilderness medicines – healthful plants of the North. Alaska Publishing, Edmonds, Washington WA. 107 p. Nienstaedt The thickness of the moss–organic layer commonly exceeds 25 cm in the far north and may approach twice that figure. The mosses compete for nutrients and have a major influence on soil temperatures in the rooting zone. Permafrost development in parts of Alaska, Yukon, and the Northwest Territories is facilitated by the insulative organic layer (Viereck 1970a, b, Gill 1975, Van Cleve and Yarie 1986).Gill, D. (1975). "Influence of white spruce trees on permafrost-table microtopography, Mackenzie River Delta." Can. J. Earth Sci. 12(2):263–272.Van Cleve, K.; Yarie, J. (1986). "Interaction of temperature, moisture, and soil chemistry in controlling nutrient cycling and ecosystem development in the taiga of Alaska." pp. 160–189 in Van Cleve, K.; Chapin, F.S.; Flanagan, P.W.; Viereck, L.A.; Dyrness, C.T. (Eds.). (1986). Forest Ecosystems in the Alaskan Taiga. Springer-Verlag, New York NY.
Especially important in determining the response of white spruce to low temperatures is the physiological state of the various tissues, notably the degree of "hardening" or dormancy. A natural progression of hardening and dehardening occurs in concert with the seasons.Glerum, C. (1985). "Frost hardiness of coniferous : principles and applications." p. 107–123 in Duryea, M.L. (Ed.). Proceedings: Evaluating seedling quality: principles, procedures, and predictive abilities of major tests. Workshop, October 1984, Oregon State Univ., For. Res. Lab., Corvallis OR. While different tissues vary in ability to tolerate exposure to stressful temperatures, white spruce, as with woody plants in general, has necessarily developed sufficient winter hardiness in its various tissues to enable them to survive the minimum temperatures experienced in the distribution range.
White spruce is subject to severe damage from spring frosts. Newly flushed shoots of white spruce are very sensitive to spring frost.Smith, B.J. (1949). "Silvicultural work at the Sault Ste. Marie Division of." Can. Pulp Paper Assoc., Woodlands Section, Woodlands Section Index No. 1050 (F-2). 4 p.Rowe, J.S. (1955). Factors influencing white spruce reproduction in Manitoba and Saskatchewan. Can. Dep. Northern Affairs and National Resources, For. Branch, For. Res. Div., Ottawa ON, Project MS-135, Silv. Tech. Note 3. 27 p.McLeod, J.W. 1964. Planting white spruce on wet brushy land. Can. Dep. For., For. Res. Branch, Ottawa ON, Publ. 1067. 4 p. This sensitivity is a major constraint affecting young trees planted without overstorey nurses in boreal climates.Sutton, R.F. (1992). "White spruce ( Picea glauca Moench Voss): stagnating boreal old-field plantations unresponsive to fertilization and weed control." For. Chron. 68:249–258.
Floodplain deposits in the Northwest Territory, Canada, are important in relation to the development of productive forest types with a component of white spruce. The most recently exposed surfaces are occupied by sandbar vegetation or riparian shrub willows and Alnus incana. With increasing elevation, the shrubs give way successively to balsam poplar and white spruce forest. In contrast, older floodplains, with predominantly brown wooded soils, typically carry white spruce–trembling aspen mixedwood forest.
Interrelationships among nutrient cycling, regeneration, and subsequent forest development on floodplains in interior Alaska were addressed by Van Cleve et al.,Van Cleve, K.; Dyrness, R.; Viereck, L. 1980. Nutrient cycling in interior Alaska flood plains. p. 11–18 in Murray, M.; Van Veldhuizen, R.M. (Eds.). Proc. Workshop, Fairbanks, Alaska, Nov. 1979. USDA, For. Serv., Pacific Northwest For. Exp. Sta., Portland OR, Gen. Tech. Rep., PNW-107. 52 p. who pointed out that the various stages in primary succession reflect physical, chemical, and biological controls of ecosystem structure and function. Thus, each successional stage has a species combination in harmony with site quality. Short-circuiting succession by planting a late successional species such as white spruce on an early successional surface may result in markedly reduced growth rates because of nitrogen insufficiency. Without application of substantial amounts of fertilizer, use would have to be made of early successional alder and its site-ameliorating additions of nitrogen.
Neiland and Viereck noted that "the slow establishment and growth of spruce under birch stands in may be partially due to effects of shading and general competition for water and nutrients, but may also be more directly related to the birch itself. HeikinheimoHeikinheimo, O. 1915. Der einfluss der brandwirtschaft auf die Wälder Finnlands. Kaskiviljelyksen Vaikutus Suomen Metsin. Acta Forest. Fenn. 4:1–264, 1–149, 1–59 GermanLutz, H.J. 1956. Ecological effects of forest fires in the interior of Alaska. USDA, For. Serv., Washington DC, Tech. Bull. 1133. 121 p. found that birch ash inhibited white spruce seedlings, and GregoryGregory, R.A. 1966. The effect of leaf litter upon establishment of white spruce beneath paper birch. For. Chron. 42:251–255. found that birch litter has a smothering effect on spruce seedlings.".Neiland, B.J.; Viereck, L.A. 1977. Forest types and ecosystems. p. 109–136 in North American Forest Lands at Latitudes North of 60 Degrees, Proc. sympos., Univ. Alaska, Fairbanks AK, Sept. 1977.
On dry upland sites, especially south-facing slopes, the mature vegetation is white spruce, white birch, trembling aspen, or a combination of these species. Succession follows in one of two general patterns. In most cases, aspen and birch develop as a successional stage after Wildfire before reaching the spruce stage. But, occasionally, with optimal site conditions and a source of seed, white spruce will invade with the or within a few years thereafter, thereby producing even-aged white spruce stands without an intervening hardwood stage.
Of the Eastern Forest Cover Types recognized by the Society of American Foresters, only one, White Spruce, names that species in its title. The eastern White Spruce Cover Type, as defined, encompasses white spruce both in pure stands, and in mixed stands "in which white spruce is the major undefined component."Payette, S. 1980. Eastern forest cover types, Boreal Forest Region: white spruce. p.15 in Eyre, F.H. (Ed.). Forest Cover Types of the United States and Canada. Soc. Amer. Foresters, Washington DC. 148 p.
In most of its range, white spruce occurs more typically in association with trees of other species than in pure stands.
White spruce is an associated species in the following Eastern Forest cover types, by the Society of American Foresters; in the Taiga Region: (1) jack pine, (5) balsam fir, (12) black spruce, (16) aspen, (18) paper birch, and (38) tamarack; in the Northern Forest Region: (15) red pine, (21) eastern white pine, (24) hemlock-yellow birch, (25) sugar maple-beech-yellow birch, (27) sugar maple, (30) red spruce-yellow birch, (32) red spruce, (33) red spruce-balsam fir, (37) northern white-cedar, and (39) black ash-American elm-red maple.Eyre, F.H. (Ed.) 1980. Forest Cover Types of the United States and Canada. Soc. Amer. Foresters, Washington DC. 148 p.
Although sometimes describedSwitzer, A.L.K. (1960). "Spruce management for the future." For. Chron. 36(2):163–165. as relatively resistant to attack by insects and disease, white spruce is far from immune to depredation. Important insect pests of white spruce include the spruce budworm ( Choristoneura fumiferana), the yellow-headed spruce sawfly ( Pikonema alaskensis), the European spruce sawfly ( Gilpinia hercyniae), the spruce bud moth ( Zeiraphera canadensis), and spruce beetle ( Dendroctonus rufipennis).Fowells, H.A. (1965). Picea (spruces). p. 287–327 in Silvics of Forest Trees of the United States. H.A. Fowells (Compiler), USDA, Forest Service, Washington DC, Agric. Handbook No. 271.Rose, A.H.; Lindquist, O.H. (1985). Insects of eastern spruces, fir and, hemlock, revised edition. Gov't Can., Can. For. Serv., Ottawa, For. Tech. Rep. 23. 159 p. (cited in Coates et al. 1994, cited orig ed 1977)Ives, W.G.H.; Wong, H.R. (1988). Tree and shrub insects of the prairie provinces. Gov't Can., Can. For. Serv., Edmonton AB, Inf. Rep. NOR-X-292. 327 p.Coates As well, other budworms, sawflies, and bark beetles, gall formers, bud midges, leaf miners, aphids, leaf eaters, leaf rollers, loopers, mites, scales, weevils, borers, pitch moths, and spittlebugs cause varying degrees of damage to white spruce.
A number of sawflies feed on spruce trees. Among them European spruce sawfly, yellow-headed spruce sawfly, green-headed spruce sawfly and the spruce webspinning sawfly.
More than a dozen kinds of looper feed on the spruces, fir, and hemlock in eastern Canada. The full-grown larvae of the larvae vary in length from 15 mm to 35 mm. Some feed briefly in the fall and complete their feeding in the spring; others feed mainly in the summer; still others feed mainly in the late summer and fall.
The fall and spring feeding group includes the dash-lined looper ( Protoboarmia porcelaria indicataria), the diamond-backed looper ( Hypagyrtis piniata), the fringed looper ( Campaea perlata), and the false loopers ( Syngrapha species). The summer feeding group includes the false hemlock looper ( Nepytia canosaria Walker), occasionally occurring in large numbers and usually in conjunction with the hemlock looper ( Lambdina fiscellaria), the Eupithecia species, the yellowlined conifer looper ( Cladara limitaria), and the saddleback looper ( Ectropis crepuscularia).
The late summer and fall group includes the common Macaria signaria ( Semiothisa signaria dispuncta) and the similar hemlock angle (moth) Macaria fissinotata on hemlock, the small spruce loopers Eupithecia species, the gray spruce looper Caripeta divisata, occasionally abundant, the black-dashed hydriomena moth ( Hydriomena divisaria), and the whitelined looper ( Eufidonia notataria).
'Conica' is a dwarf conifer with very slender leaves, like those normally found only on one-year-old seedlings, and very slow growth, typically only per year. Older specimens commonly 'revert', developing normal adult foliage and starting to grow much faster; this 'reverted' growth must be pruning if the plant is to be kept dwarfing.
The wood is also exported to Japan where, known as "shin-kaya", it is used to make as a substitute for the rare Torreya nucifera wood. Additionally, Picea glauca var. densata is used for bonsai.
White spruce is the provincial tree of Manitoba
The new growth or tips of white spruce is used in beer making, gin production, flavouring soda, candy making or in pickles and preserves.
Seeds
- Zasada, J.C.; Foote, M.J.; Deneke, F.J.; Parkerson, R.H. 1978. Case history of an excellent white spruce cone and seed crop in interior Alaska: cone and seed production, germination and seedling survival. USDA, For. Serv., Pacific NW For. Range Exp. Sta., Portland OR, Gen. Tech. Rep. PNW-65. 53 p.
Root system
Stem
Bark
Chemistry
Varieties
Distribution and habitat
As an exotic species
Ecology
Soils
-Lafond, A. (1954). Les déficiences en potassium et magnésium des plantations de Pinus strobus, Pinus resinosa et Picea glauca de la province de Québec. Assoc. Ing. For. Prov. Québec, Texte des Conf. 34 Assemb. Ann.:65–82.
- McLeod, J.W. 1956. Plantations of the Acadia Forest Experiment Station. Can. Dep. Northern Affairs National Resour., For. Branch, For. Res. Div., Ottawa ON, Tech. Note 31. 25 p.
- MacArthur, J.D. 1957. The effects of manure on a white and Norway spruce plantation at Grand'Mère, Quebec. Can. Dep. Northern Affairs National Resour., For. Branch, For. Res. Div., Ottawa ON, Tech. Note 64. 15 p.
- Paine, L.A. 1960. Studies in forest pathology. XXII. Nutrient deficiencies and climatic factors causing low volume production and active deterioration in white spruce. Can. Dep. Agric., For. Biol. Div., Ottawa ON, Publ. 1067. 29 p.
- Swan, H.S.D. 1960. The mineral nutrition of Canadian pulpwood species. 1. The influence of nitrogen, phosphorus, potassium and magnesium deficiencies on the growth and development of white spruce, black spruce, jack pine and western hemlock seedlings grown in a controlled environment. Pulp Paper Res. Instit. Can., Montreal QC, Woodlands Res. Index No. 116, Tech. Rep. 168. 66 p. Minimum soil-fertility standards recommended for white spruce sufficient to produce 126 to 157 m3/ha of wood at 40 years are much higher than for pine species commonly planted in the Lake States (Wilde 1966):Wilde, S.A. (1966). "Soil standards for planting Wisconsin conifers." J. For. 64(6):389–391. 3.5% organic matter, 12.0 meq/100 g exchange capacity, 0.12% total N, 44.8 kg/ha available P, 145.7 kg/ha available K, 3.00 meq/100 g exchangeable Ca, and 0.70 meq/100 g exchangeable Mg.
Cold hardiness
Forest succession
Associated forest cover
Predators
Cultivars
Uses
External links
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