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You are here >1Up Info > Wildlife, Animals, and Plants > Plant Species > Tree > Species: Quercus velutina | Black Oak
 

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BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Quercus velutina | Black Oak
GENERAL BOTANICAL CHARACTERISTICS : Black oak is a medium- to large-sized, native, deciduous tree with an irregularly rounded crown [56]. In a forest, the trunk is usually branch-free for half the height of the tree [28]. Individuals may live 150 to 200 years. On good sites, black oak may reach 150 feet (46 m) in height and 48 inches (122 cm) in d.b.h., but most trees are 60 to 80 feet (18-24 m) tall and 24 to 36 inches (61-91 cm) in d.b.h. [56]. Black oak has a deep taproot and deep and widespreading lateral roots [28]. RAUNKIAER LIFE FORM : Phanerophyte REGENERATION PROCESSES : Sexual: Black oak is monoecious. Seed production begins when the tree is about 20 years old, with maximum production occurring between ages 40 and 75. Black oak is a consistent seed producer, with good acorn crops every 2 to 3 years. Seed dissemination is by squirrels, mice, bluejays, and other animals, and by gravity. Rodents and birds often cache acorns in the soil [56]. Germination is hypogeal. Burial in or contact with mineral soil and coverage with a light layer of leaves are favorable conditions for acorn germination [56]. In a study of black oak and white oak regeneration of an old field in Michigan, seedlings were more likely to establish initially in open patches because blue jays preferentially choose open sites to cache acorns. However, seedlings that colonized open patches were not likely to survive beyond the first several years unless the patch was subsequently invaded by herbaceous vegetation [24]. Seedling growth is slow; average annual height growth of seedlings in Missouri during a 6-year period was 2.1 inches (5.3 cm) [35]. Seedlings can survive drought conditions [56]. Vegetative: Black oak sprouts from the root collar if top-killed or cut. Younger individuals are more likely to sprout than older individuals. The probability that a stump with a 1-year-old sprout will have at least one dominant or codominant sprout at age 5 is predictable from stump diameter. The probability ranges from 1.0 for 3-inch (7.6 cm) stump diameters to 0.15 for 30-inch (76 cm) stump diameters [56]. Black oak has a low tolerance for multiple sprouts and tends toward the survival of a single sprout per stump. In one study, 5, 15, and 25 years after cutting, the average number of sprouts per stump was 7.5, 2.2, and 1.0 respectively [42]. Seedlings often die back and sprout numerous times, thus becoming advance regeneration. The roots of black oak saplings may be 10 to 20 years older than the tops [56]. Sprouts grow faster than seedlings. Average annual height growth of sprouts in Missouri during a 6-year period was 6.1 inches (15.5 cm) [35]. Generally, the bigger the old stem is, the faster the height growth of its sprouts [56]. SITE CHARACTERISTICS : Black oak, an upland xerophytic species, can occur on all aspects and slope positions, but tends to be more abundant on the drier southerly and westerly aspects and on upper slopes and ridges [16,56]. Black oak does not appear to be site-sensitive. Its occurrence is more due to fortuitous circumstance than inherent habitat requirements [16]. Although it grows best on moist, rich, well-drained sites, it is sensitive to competition on these sites and is more often found on dry, nutrient-poor, coarse-textured soils [56]. Black oak does not occur on the serpentine soils of the Maryland Piedmont [68]. It often grows on sandy or gravelly sites or heavy glacial clay hillsides. Black oak is found up to 4,000 feet (1,200 m) in the southern Appalachian Mountains [56]. Black oak is less drought tolerant than post oak (Q. stellata), but more tolerant than northern red oak and about as tolerant as white oak [57]. Its predominance on southerly and westerly aspects may be due in part to drought tolerance. In addition, the increased solar radiation on these sites may facilitate early establishment and eventual dominance of black oak [49]. Overstory associates of black oak not mentioned in Distribution and Occurrence include pignut hickory (Carya glabra), mockernut hickory (C. tomentosa), bitternut hickory (C. cordiformis), shagbark hickory (C. ovata), American elm (Ulmus americana), slippery elm (U. rubra), white ash (Fraxinus americana), black walnut (Juglans nigra), butternut (J. cinerea), southern red oak, scarlet oak, chinquapin oak (Q. muehlenbergii), red maple (Acer rubrum), black cherry, and blackgum (Nyssa sylvatica) [56]. Common small tree associates include sassafras, flowering dogwood (Cornus florida), sourwood (Oxydendron arboreum), eastern hophornbeam (Ostrya virginiana), redbud (Cercis canadensis), pawpaw (Asimina triloba), downy serviceberry (Amelanchier arborea), and American bladdernut (Staphylea trifolia) [56]. Common shrub associates include blueberry (Vaccinium spp.), mountain-laurel (Kalmia latifolia), witch-hazel (Hamamelis virginiana), beaked hazel (Corylus cornuta), spicebush (Lindera benzoin), sumac (Rhus spp.), and Viburnum spp. [56]. Herbaceous plants associated with black oak in sand savannas include little bluestem (Schizachyrium scoparius), Pennsylvania sedge (Carex pensylvanica), and Coreopsis spp. [8]. SUCCESSIONAL STATUS : Facultative Seral Species Black oak is intermediate in shade tolerance. It is more tolerant than black cherry or shortleaf pine (Pinus echinata), but less tolerant than white oak, chestnut oak (Quercus prinus), hickories, maples (Acer spp.), elms (Ulmus spp.), beech (Betula spp.), or blackgum. Light is required to recruit black oak seedlings into the sapling stage; seedlings eventually die under a closed-canopy forest [29,56]. Black oak replaces pines (Pinus spp.) on heavily cutover areas. It succeeds sassafras and common persimmon (Diospyros virginiana) on upland old fields [16]. In the Hudson River Valley in New York, stands dominated by white oak, black oak, and pignut hickory occur on rocky, nutrient-poor sites. The open canopy, less distinct vertical stratification of canopy trees, and diverse herbaceous understory suggest these forests gradually invade old pasture sites [18]. Black oaks woodlands began invading savannas in Northern Illinois 2 to 3 years after the construction of roads which acted as functional firebreaks [50]. In the past, the high presettlement fire frequency in grasslands prevented black oak expansion [1] The importance of black oak in many forests has declined since human settlement. In the absence of disturbance such as fire or windthrow, black oak is succeeded by more shade-tolerant, mesophytic species. A decline in black oak has been documented in an old-growth oak-hickory forest in southwestern Illinois. Black oak had been dominant in the forest since 1821, but it decreased in density and basal area between 1956 and 1983 due to senescence. Sugar maple (Acer saccharum) has increased in the forest. It is believed that black oak originally established on this site after the New Madrid Earthquake in 1811 or after a hurricane shortly after the earthquake, both of which caused much downed timber [59]. In the late 1700's and 1800's in Pennsylvania, massive logging to provide wood for charcoal-fueled iron furnaces was accompanied by wildfires. The combination of logging and fire increased the relative dominance of oaks, including black oak. In the 20th century, fire was suppressed and eventual logging of stands with understories dominated by red maple, sugar maple, and black cherry accelerated the recruitment of these mesophytic species into the canopy [2]. In the Hudson River valley in New York, early land surveys indicate the white oak-black oak-hickory type was prevalent prior to forest clearing. Since abandonment from agriculture, the type has returned but is not nearly as important as it was. The percent occurrence of black oak in these forests was 15.3 percent in the period before 1800 and only 4.1 percent in 1984 [18]. In a black oak-white oak forest in southern Wisconsin, white oak is replacing black oak. Black oak, which is more susceptible to oak wilt than white oak, is dying. White oak is not regenerating in the forest but because it is a longer lived, slower growing species, it is now replacing black oak [41]. Succession is slow or unlikely in some oak forests on extremely xeric or nutrient poor sites [1]. Blackjack oak and black oak forests on extremely xeric, upland sites in Illinois did not exhibit signs of being replaced by late successional species. Self-maintenance was evident as blackjack oak and black oak were important species in the sapling and seedling layers as well as the overstory [3]. Even in the absence of fire, succession towards a richer, mesophytic forest appears slow or unlikely in a black oak-blueberry community on the Lake Michigan sand dunes. Black oak has low nutrient requirements and is relatively ineffective in returning nutrients to the dune surface in its litter. The well-leached dunes remain dry and nutrient poor. Fire aggrevates these conditions and helps perpetuate black oak on these sites [52]. Some of the most xeric sites of the South Carolina Piedmont are occupied by old-growth communities of black oak, post oak, and blueridge blueberry (Vaccinium vacillans). Although the community appears to be in steady state, it may evolve into a hickory-dominated community in the absence of fire [30]. SEASONAL DEVELOPMENT : Staminate flowers develop from leaf axils of the previous year. Catkins emerge before or at the same time as the current year's leaves, usually in April or May. Acorns mature in two growing seasons. The acorns ripen from late August to October depending on geographic location, drop in the fall, and germinate in the spring [56].

Related categories for Species: Quercus velutina | Black Oak

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Information Courtesy: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory. Fire Effects Information System

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