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Introductory

SPECIES: Quercus macrocarpa | Bur Oak
ABBREVIATION : QUEMAC SYNONYMS : Quercus mandanensis SCS PLANT CODE : QUMA2 COMMON NAMES : bur oak blue oak mossycup oak mossy-overcup oak scrub oak TAXONOMY : The fully documented scientific species name is Quercus macrocarpa Michx. Widely recognized varieties are [14]: Q. m. var. depressa (Nutt.) Engelm. Q. m. var. olivaeformis (Michx. f.) A. Gray Q. m. var. macrocarpa Bur oak is a member of the white oaks (Lepidobalanus) [20].. This subgenus is noted for widespread hybridization and many intermediate forms. Bur oak hybridizes with numerous species including northern pin oak (Q. ellipsoidalis), white oak (Q. alba), swamp white oak (Q. bicolor), overcup oak (Q. lyrata), swamp chestnut oak (Q. michauxii), chinkapin oak (Q. muehlenbergii), post oak (Q. stellata), live oak (Q. virginiana), and Gambel oak (Q. gambelii) [19,20,35]. LIFE FORM : Tree FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : D. Tirmenstein, January 1988 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Tirmenstein, D. 1988. Quercus macrocarpa. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Quercus macrocarpa | Bur Oak
GENERAL DISTRIBUTION : Bur oak is widely distributed throughout much of the north-central United States and the eastern Great Plains [40]. It occurs from southern New Brunswick and New England westward to the Dakotas and southeastern Montana, and south to Texas, Arkansas, and Tennessee [10,19]. Bur oak is locally common in Louisiana and Alabama [19]. Quercus macrocarpa var. olivaeformis is largely restricted to Iowa, Minnesota, South Dakota, and North Dakota. Quercus macrocarpa var. depressa occurs mostly along the western margin of the Great Plains [14]. ECOSYSTEMS : FRES15 Oak - hickory FRES17 Elm - ash - cottonwood FRES21 Ponderosa pine FRES29 Sagebrush FRES38 Plains grasslands FRES39 Prairie STATES : AL AR CT DE IL IN IA KS KY LA ME MD MI MN MO MT NE NH NJ NY ND OH OK PA RI SD TN TX VT VA WV WI WY MB NB ON PQ SK ADMINISTRATIVE UNITS : BUFF CUVA DETO EFMO FODO GWCA MACA MORU OZAR PIPE ROCR THRO VOYA WICR WICA BLM PHYSIOGRAPHIC REGIONS : 14 Great Plains 15 Black Hills 16 Upper Missouri Basin and Broken Lands KUCHLER PLANT ASSOCIATIONS : K011 Western ponderosa forest K016 Eastern ponderosa forest K017 Black Hills pine forest K056 Wheatgrass - needlegrass shrubsteppe K064 Grama - needlegrass - wheatgrass K066 Wheatgrass - needlegrass K067 Wheatgrass - bluestem - needlegrass K070 Sandsage - bluestem prairie K074 Bluestem prairie K081 Oak savanna K098 Northern floodplain forest SAF COVER TYPES : 236 Bur oak 237 Interior ponderosa pine SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Bur oak is an important dominant in many plant communities. Publications naming bur oak in habitat type, community type, or plant asociation classifications are: Classification of the forest vegetation of Wyoming [2] Upland hardwood habitat types in southwestern North Dakota [13] Upland forest and woddland habitat of the Missouri Plateau, Great Plains Province [15] Forest vegetation of the Routt National Forest in northwestern Colorado: a habitat classification [16] Plant assocaitions of Region 2: Potential plant communities of Wyoming, South Dakota, Nebraska, Colorado, and Kansas [17] Composition and structure of the principle woody vegetation types in the North Dakota Badlands [22] A classification of the Cercocarpus mantanus, Quercus macrocarpa, Populus deltoides, & Picea glauca habitat types of the Black Hills NF [32]

VALUE AND USE

SPECIES: Quercus macrocarpa | Bur Oak
WOOD PRODUCTS VALUE : Bur oak is harvested for timber from bottomlands of Iowa and Illinois [7]. IMPORTANCE TO LIVESTOCK AND WILDLIFE : Bur oak provides food and cover for wildlife species [40]. The foliage is a common and important constituent of cattle diets in the Black Hills, South Dakota [37,38]. Foliage is also an important food for white-tailed deer in the Black Hills [37]. Cattle, horses, and sheep eat the seedlings [34]. Many birds and mammals eat bur oak acorns including squirrels, deer, wood ducks, blue jays, and cows [25,37,42]. Rodents and blue jays frequently cache the acorns for later use, thereby facilitating seed dispersal. PALATABILITY : Bur oak is somewhat palatable to many species of wildlife and domestic livestock. It provides forage during much of the year for both mule deer and cattle in the Black Hills of South Dakota [37,40]. Average comsuption for cattle in the Black Hills was [38]: June 13.2% July 8.7% August 12.2% September 12.4% Cattle may prefer browsing bur oak. Although cover of bur oak at one South Dakota site was only estimated at 1.5 percent, it comprised 12.2 percent of the cattle's diet in August [38]. Young seedlings may be palatable to cattle, horses, and sheep [34]. The degree of use shown by livestock and wildlife species for bur oak in North Dakota and Wyoming is [7]: ND WY Cattle Poor Poor Sheep Fair Fair Horses Poor Poor Pronghorn Fair Poor Bighorn ---- ---- Elk ---- Fair Mt. goat ---- ---- Mule deer Good Good White-tailed deer Good Good Small mammals Good Good Small nongame birds Poor Good Upland game birds ---- Good Waterfowl ---- Poor NUTRITIONAL VALUE : Bur oak is poor energy and protein value [7]. General nutritional data for the genus Quercus are [21]: Oak leaves Acorns Acorn meats Dry matter - % 100.0 100.0 100.0 Organic matter - % ----- 97.5 98.0 Ash - % 5.6 2.5 2.0 Crude fiber - % 27.4 13.9 2.0 Ether extract - % 2.5 5.4 8.9 N-free extract - % 54.3 73.5 80.7 Protein (nx6.25)% 10.2 4.8 6.4 Cattle-dig. protein - % 5.8 0.5 1.9 Goats-dig. protein - % 6.1 1.7 3.1 Horses-dig. protein - % 6.2 1.7 3.1 Sheep-dig. protein - % 5.7 1.7 3.1 Nutritional data for whole bur oak acorns are [7]: Chemical content of whole acorns (%) Crude Total Total P Ca Mg fat carbohydrates protein 4.8 45.9 4.3 0.10 0.08 0.06 COVER VALUE : Bur oak provides hiding cover and nesting sites for many birds and mammals. Red-tailed hawks, screech owls, fox squirrels, and flying squirrels nest in large bur oaks [34]. The degree to which bur oak provides environmental protection during one or more seasons for several wildlife species is [7]: ND WY Pronghorn Poor Poor Bighorn ---- ---- Elk ---- Good Mt. goat ---- ---- Mule deer Good Good White-tailed deer Good Good Small mammals Good Good Small nongame bird Good Good Upland game birds ---- Good Waterfowl ---- Poor VALUE FOR REHABILITATION OF DISTURBED SITES : Bur oak has been widely tested for use in rehabilitation. It has been successfully planted on coal spoils in the north-central and northern Great Plains, and in the Western Interior Coal Province which encompasses Missouri, Kansas, and Oklahoma [40]. Bur oak may be either seeded or transplanted onto disturbed areas. Seeds should be planted in groups of two or three, 0.5 to 1 inch (1.2 to 2.5 cm) deep, at a density of 900 to 1,000 per acre. Recommended spacing is 6 feet by 6 feet by 7 feet (1.8 m x 1.8 m x 2.1 m). Acorns average 45 percent germination with 75 seeds per pound [40]. Acorns are frequently stratified under cold moist conditions for 1 to 2 months prior to planting [40], although stratification is not required [45]. Direct seeding is usually carried out during the fall in the Western Interior Coal Province [40], although seed may be planted in either the spring or fall. Seed may be hand broadcast, hand drilled, or mechanically broadcast. Mulching aids the germination of seed planted in the fall [45]. Most seed germination occurs during the fall, but Quercus macrocarpa var. olivaeformis typically germinates during the spring [40]. OTHER USES AND VALUES : Bur oak is extremely tolerant of city smoke and other air pollutants [43]. It has been widely planted in Minneapolis and other urban areas [39], and is commonly planted as a shade tree in many other areas of the United States [42]. MANAGEMENT CONSIDERATIONS : Bur oak sprouts vigorously following cutting of pole-size or smaller trees. Larger trees may also produce some sprouts [7]. Chemical control of bur oak is difficult [44].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Quercus macrocarpa | Bur Oak
GENERAL BOTANICAL CHARACTERISTICS : Bur oak is a spreading, deciduous, large shrub to large tree [20,40]. On eastern forested sites, it is typically a large tree and reaches up to 100 feet (31 m) in height and 3 to 4 feet (0.9 to 1.2 m) or more in diameter [40]. Bur oak grows best on the rich bottomlands of southern Illinois and Indiana, where it may reach 170 feet (52 m) with a diameter of 6 to 7 feet (1.8 to 2.1 m) [34]. On rocky bluffs with thin soil and at the north and west ends of its range, bur oak more commonly grows as a small tree or large shrub [20]. On poor soil along the top of bluffs at the western edge of its range, it often forms dense thickets of low straggling shrubs which may reach only 1.7 to 3.3 feet (5 to 10 dm) in height [34]. Twigs are thick and corky [40,43]. Branches are low and stout, and the crown is generally open, broad, and round [40]. Leaves are variable, although generally large (2-10 in [5-25 cm] long), and deeply divided into five to nine rounded lobes [14]. Staminate flowers are borne in small, pendant catkins, and solitary to few pistillate flowers are in the leaf axils. Fruits are relatively large acorns up to 2 inches (5.1 cm) in length. They are partly or entirely enclosed in a fringed or "mossy" cap [40]. Roots have great tensile strength [41]. The well-branched, widely spreading roots allows growth in dry areas [41]. Bur oak is slow growing and long lived, sometimes reaching 200 or 300 years of age [34,41]. RAUNKIAER LIFE FORM : Phanerophyte REGENERATION PROCESSES : Bur oak reproduces both sexually and vegetatively. Trees are wind pollinated [25]. Pollen from one tree germinates better on the stigmas of a second tree, favoring cross-pollination [46]. Minimum seed-bearing age is 35, with optimum seed production occurring between 75 and 150 years of age [46]. Acorns are produced in abundance every 2 to 3 years with light crops in intervening years [23,45]. Seeds mature within 1 year [46]. When conditions are favorable, acorns germinate immediately after dropping from the tree [25]. Seed is dispersed primarily by gravity and small mammals, with water playing a lesser role [4]. Although most bur oak acorns germinate in the fall, acorns of Q. m. var. olivaeformis, a northern variety, usually germinate in spring [46]. Germination under laboratory conditions ranged from 45 to 99 percent, although much variation has been noted [3,23,46]. The acorns do not have a dormancy period [40]. Acorns are extremely vulnerable to predation by insects, small birds and mammals, and unless germination is rapid, few seeds survive [25]. Studies in Iowa uplands have shown that bur oak germination is best when litter is removed. Litter-covered acorns appear to be more vulnerable to rodents, insects, and fungus [46]. Under laboratory conditions, acorns are generally pretreated by 1 to 2 months of stratification prior to planting and are subjected to alternating temperatures of 68 and 86 degrees Fahrenheit (20-30 deg C) [30,40]. Stratification is apparently not required for good germination, however. Seed is stored over winter in a cool, moist place at 33 to 40 degrees F (0.6-4 degrees C) [45]. Under some conditions, bur oak produces plural-seeded acorns which result in poor germination or weak and misshapen seedlings [7]. The production of plural-seeded acorns is believed to be genetically controlled, although modifications brought about by environmental conditions may also contribute to their production [3]. High production of plural-seeded acorns at a particular site may result in decreased seedling production. Bur oak taproots grow rapidly. They reach approximately 9 inches (22.9 cm) before leaves unfold [41]. In many areas, relatively few seedlings are produced from acorns [34], and vegetative regeneration is much more common. Bur oak sprouts vigorously after fire or other disturbance. It sprouts prolifically from the root crown when the main stem is damaged [28]; however, stump sprouting has also been well documented [31,40]. Pole-sized or smaller trees sprout well after burning or cutting, although the quality and form of sprouts is described as "relatively poor" [46]. Larger trees also produce some sprouts. The relationship between the size, age, and vigor of the parent and its ability to sprout is unknown [46]. SITE CHARACTERISTICS : Bur oak grows in a range of habitats from upland woods to valley floors [11]. It occurs throughout the southern hardwood forests and through much of the northeastern hardwood forests [34]. Bur oak is a prominent constituent of oak-basswood (Quercus spp.-Tilia americana) forests, upland oak-hickory (Quercus macrocarpa, Q. borealis, Carya cordiformis, and Ostrya virginia) forests, mixed-oak communities (Quercus spp.), and is transitional to sugar maple-basswood (Acer saccharum-Tilia americana) communities of the upper Midwest [6,28]. This species commonly forms nearly pure savannas, occasionally interspersed with white oak (Quercus alba). Bur oak savannas were formerly much more abundant, but have declined due to grazing and fire suppression [34]. Soils: Bur oak tolerates a wide range of soil types. It commonly grows on medium to somewhat coarsely-textured soils, and more rarely on clays. It is well adapted to fairly acidic (>4.0 pH) to moderately basic, nonsaline soils [40]. Optimum soil depth is greater than 20 inches (51 cm) [7]. It thrives on the moist flats and bottomlands along the Ohio River and grows well on shallow uplands and bluffs on soils derived from limestone [40]. Moisture regime: Bur oak is well adapted to growth on moist, rich bottomlands with sufficient, but not excessive, amounts of water [34]. It is intolerant of flooding and may be killed by floods during the growing season [40]. It grows in areas receiving 15 to 40 inches (38 to 102 cm) maximum annual precipitation but does best where maximum annual precipitation averages 30 to 40 inches (76 to 102 cm) [43]. Associates: Species commonly growing in association with bur oak include boxelder (Acer negundo), black ash (Fraxinus nigra), white ash (F. americana), red maple (Acer rubrum), shellbark and bitternut hickories (Carya laciniata, C. cordiformis), American elm (Ulmus americana), hackberries (Celtis spp.), eastern cottonwood (Populus deltoides), black locust (Robinia pseudoacacia), basswood (Tilia americana), northern red oak (Q. aborealis), northern pin oak (Q. ellipscidalis), white oak (Q. alba), and swamp white oak (Quercus bicolor) [26,28,34,40]. Elevation: Elevational ranges of bur oak are as follows [6]: from 3,200 to 3,500 ft (976 to 1,068 m) in MT 3,200 to 3,200 ft (976 to 976 m) in WY SUCCESSIONAL STATUS : Facultative Seral Species Bur oak may have climax or seral status depending on the site. In many dry, exposed areas of Wisconsin, it is a climax species. It is also a climax species in most areas of the Black Hills [32]. Bur oak is an early seral species in many mesic forest habitats of Wisconsin [32]. In many areas, this species, which is moderately intolerant of shade, is replaced by more shade-tolerant hardwoods [40]. Bur oak is a pioneer at prairie margins [40], and is a pioneer or early seral species after fire in the Black Hills [32]. In parts of Minnesota where fire is suppressed, bur oak is replaced by maple (Acer spp.) or basswood (Tilia americana) communities [6,31]. SEASONAL DEVELOPMENT : Bur oak flowers shortly after leaves develop, but prior to or early in the period of major stem expansion [1,40]. Initiation of flowers and leaves in the spring is not closely related to temperature [1]. Flowering usually begins in April in the South, but may not begin until June in the North [40]. In North Dakota, trees flowers from May through June [46]. Acorns ripen from August to November [40]. Most seed dispersal takes place from August to September [45]. The following sequence of phenological development was recorded during a 6-year observation period in northeastern Minnesota [1]: Phenology 1951 - 1956 Bud Leaf Flowering Pollen Seed fall earliest date 4/24 5/11 5/12 5/23 ---- latest date 5/21 5/25 6/2 6/8 10/3 Leaf color Leaf fall Cambial activity change Init. End earliest date 9/13 9/26 5/15 7/16 latest date 9/19 10/14 5/29 8/23

FIRE ECOLOGY

SPECIES: Quercus macrocarpa | Bur Oak
FIRE ECOLOGY OR ADAPTATIONS : Bur oak bark is thick and fire resistant [6,40]. Larger trees often survive fire [31,34,40]. Bur oak sprouts vigorously from the stump or root crown after fire [28,31]. It sprouts most prolifically from pole-size or smaller trees, although larger trees may produce some sprouts [46]. In many areas, bur oak communities may be favored by fire [16,25]. Without fire, seedlings of bur oak are unable to compete with other, more shade-tolerant species [25]. Bur oak communities may be replaced by more shade-tolerant maple-basswood (Acer spp.-Tilia spp.) forests with in the absence of fire [6,31]. Smaller bur oaks can be reduced or eliminated by frequent burning if sufficient fuels are available [29]. POSTFIRE REGENERATION STRATEGY : Survivor Species; on-site surviving root crown or caudex Survivor Species; on-site surviving rhizomes Off-site Colonizer; seed carried by animals or water; postfire yr 1&2

FIRE EFFECTS

SPECIES: Quercus macrocarpa | Bur Oak
IMMEDIATE FIRE EFFECT ON PLANT : Bur oak has a thick, fire-resistant bark at maturity [6]. Although seedlings are often killed by fire, older trees generally survive [31]. A hot, fast fire in Minnesota oak savanna removed litter and resulted in a dark charred surface, but did not kill mature trees [35]. Small grass fires are relatively common in some bur oak savannas, and typically kill only young trees [31]. In parts of northern Minnesota, mature oaks are usually killed only by "severe" fire [6]. Seedlings may be killed by annual burning where adequate fuels are present [29]. In some locations in Wisconsin, up to 10-year intervals between fires may be necessary in order for fuel build-up to reach the point where fires are hot enough to eliminate bur oak seedlings [39]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Bur oak sprouts from stumps or root crowns, even when severely damaged by fire [31]. Pole-size or smaller trees sprout vigorously when burned, but sprouting of larger trees is often less vigorous. With the exception of seedling sprouts, the quality and form of bur oak sprout stems are relatively poor [46]. Bur oak is generally favored by fire [6,16]. It sprouts vigorously when old growth maple-basswood (Acer spp.-Tilia spp.) forests are removed by fire [6,31]. In many locations, unless fire or other disturbance occurs, the bur oak seedlings are unable to compete with more shade-tolerant species [25]. On some sites in the Black Hills, bur oak sprouts may compete well with ponderosa pine seedlings (Pinus ponderosa), and pine encroachment of the burned-over area is often very slow [16]. Bur oak may grow to a large size after fire because of its competitive advantage on these sites [6]. Annual burning on sites where trees are relatively large and adequate fuels are present can prevent bur oak from increasing [29]. On other sites, an interval of up to 10 years between fires may be necessary to allow for the build-up of sufficient fuels for fire to reduce oak trees to shrubs and eliminate tree seedlings [39]. Bur oak retained preburn densities following fire in Wisconsin pine barrens, although hot fires did reduce oak average size. Average frequency of bur oak on burned plots was 28 percent and was 16 percent on unburned plots [39]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

REFERENCES

SPECIES: Quercus macrocarpa | Bur Oak
REFERENCES : 1. Ahlgren, C. E. 1957. Phenological observations of nineteen native tree species in northeastern Minnesota. Ecology. 38(4): 622-628. [74] 2. Alexander, Robert R. 1986. Classification of the forest vegetation of Wyoming. Res. Note RM-466. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 10 p. [304] 3. Beck, Allan R.; Weigle, Jack L. 1970. Plural-seeded acorns in bur oak (Quercus macrocarpa Michx.). HortScience. 5(1): 10-11. [3282] 4. 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] 5. Bonner, F. T.; Vozzo, J. A. 1987. Seed biology and technology of Quercus. Gen. Tech. Rep. SO-66. New Orleans, LA: U.S. Department of Agriculture, Forest Service, Southern Forest Experiment Station. 21 p. [3248] 6. Daubenmire, Rexford F. 1936. The "big woods" of Minnesota: its structure, and relation to climate, fire, and soils. Ecological Monographs. 6(2): 233-268. [2697] 7. Dittberner, Phillip L.; Olson, Michael R. 1983. The plant information network (PIN) data base: Colorado, Montana, North Dakota, Utah, and Wyoming. FWS/OBS-83/86. Washington, DC: U.S. Department of the Interior, Fish and Wildlife Service. 786 p. [806] 8. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 9. Fowells, H. A., compiler. 1965. Silvics of forest trees of the United States. Agric. Handb. 271. Washington, DC: U.S. Department of Agriculture, Forest Service. 762 p. [12442] 10. Garrison, George A.; Bjugstad, Ardell J.; Duncan, Don A.; [and others]. 1977. Vegetation and environmental features of forest and range ecosystems. Agric. Handb. 475. Washington, DC: U.S. Department of Agriculture, Forest Service. 68 p. [998] 11. Gartner, F. Robert; Thompson, Wesley W. 1973. Fire in the Black Hills forest-grass ecotone. In: Proceedings, annual Tall Timbers fire ecology conference; 1972 June 8-9; Lubbock, TX. No. 12. Tallahassee, FL: Tall Timbers Research Station: 37-68. [1002] 12. Girard, Michele Marie. 1985. Native woodland ecology and habitat classification of southwestern North Dakota. Fargo, ND: North Dakota State University. 314 p. Dissertation. [1025] 13. Girard, Michele M.; Goetz, Harold; Bjugstad, Ardell J. 1987. Factors influencing woodlands of southwestern North Dakota. Prairie Naturalist. 19(3): 189-198. [2763] 14. Great Plains Flora Association. 1986. Flora of the Great Plains. Lawrence, KS: University Press of Kansas. 1392 p. [1603] 15. 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] 16. Hoffman, George R.; Alexander, Robert R. 1987. Forest vegetation of the Black Hills National Forest of South Dakota and Wyoming: a habitat type classification. Res. Pap. RM-276. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 48 p. [1181] 17. Johnston, Barry C. 1987. Plant associations of Region Two: Potential plant communities of Wyoming, South Dakota, Nebraska, Colorado, and Kansas. 4th ed. R2-ECOL-87-2. Lakewood, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Region. 429 p. [3519] 18. 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] 19. 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. [2952] 20. Maze, Jack. 1968. Past hybridization between Quercus macrocarpa and Quercus gambelii. Brittonia. 20: 321-333. [1559] 21. National Academy of Sciences. 1971. Atlas of nutritional data on United States and Canadian feeds. Washington, DC: National Academy of Sciences. 772 p. [1731] 22. Nelson, Jack Raymond. 1961. Composition and structure of the principal woody vegetation types in the North Dakota Badlands. Fargo, ND: North Dakota State University. 195 p. Thesis. [161] 23. Olson, David F., Jr. 1974. Baccharis L. baccharis. 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: 244-246. [7463] 24. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 25. Reichman, O. J. 1987. Forests. In: Konza Prairie: A tallgrass natural history. Lawrence, KS: University Press of Kansas: 115-124. [4255] 26. Rothenberger, Steven J. 1985. Community analysis of the forest vegetation in the lower Platte River Valley, eastern Nebraska. Prairie Naturalist. 17(1): 1-14. [2031] 27. Rowe, J. S. 1983. Concepts of fire effects on plant individuals and species. In: Wein, Ross W.; MacLean, David A., eds. SCOPE 18: The role of fire in northern circumpolar ecosystems. Chichester; New York: John Wiley & Sons: 135-154. [2038] 28. Severson, Kieth E.; Boldt, Charles E. 1977. Problems associated with management of native woody plants in the western Dakotas. In: Johnson, Kendall L., editor. Wyoming shrublands: Proceedings, 6th Wyoming shrub ecology workshop; 1977 May 24-25; Buffalo, WY. Laramie, WY: Shrub Ecology Workshop: 51-57. [2759] 29. Smith, E. F.; Owensby, C. E. 1973. Effects of fire on true prairie grasslands. In: Proceedings, annual Tall Timbers Fire Ecology Conference; 1972 June 8-9; Lubbock, TX. No. 12. Tallahassee, FL: Tall Timbers Research Station: 9-22. [2168] 30. Sopp, D. F.; Salac, S. S.; Sutton, R. K. 1977. Germination of Gambel oak seed. Tree Planter's Notes. 28(2): 4-5. [2197] 31. Stallard, Harvey. 1929. Secondary succession in the climax forest formations of northern Minnesota. Ecology. 10(4): 476-547. [3808] 32. Steinauer, Gerald A. 1981. A classification of the Cercocarpus montanus, Quercus macrocarpa, Populus deltoides, & Picea glauca habitat types of the Black Hills NF. Vermillion, SD: University of South Dakota. 95 p. Thesis. [86] 33. Stickney, Peter F. 1989. Seral origin of species originating in northern Rocky Mountain forests. Unpublished draft on file at: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Laboratory, Missoula, MT; RWU 4403 files. 7 p. [20090] 34. Stout, A. B. 1944. The bur oak openings in southern Wisconsin. Transactions of the Wisconsin Academy of Science. 36: 141-161. [264] 35. Tester, John R. 1965. Effects of a controlled burn on small mammals in a Minnesota oak-savanna. American Midland Naturalist. 74(1): 240-244. [279] 36. U.S. Department of Agriculture, Soil Conservation Service. 1982. National list of scientific plant names. Vol. 1. List of plant names. SCS-TP-159. Washington, DC. 416 p. [11573] 37. Uresk, Daniel W.; Lowrey, Dennis G. 1984. Cattle diets in the central Black Hills of South Dakota. 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 Pub. No. 111. Rapid City, SD: South Dakota School of Mines and Technology: 50-52. [2400] 38. Uresk, Daniel W.; Paintner, Wayne W. 1985. Cattle diets in a ponderosa pine forest in the northern Black Hills. Journal of Range Management. 38(5): 440-442. [2401] 39. Vogl, Richard J. 1971. Fire and the northern Wisconsin pine barrens. In: Proceedings, annual Tall Timbers Fire ecology conference; 1970 August 20-21; New Brunsick, Canada. No. 10. Tallahassee, FL: Tall Timbers Research Station: 175-209. [2432] 40. Wasser, Clinton H. 1982. Ecology and culture of selected species useful in revegetating disturbed lands in the West. FWS/OBS-82/56. Washington, DC: U.S. Department of the Interior, Fish and Wildlife Service, Office of Biological Services, Western Energy and Land Use Team. 347 p. Available from NTIS, Springfield, VA 22161; PB-83-167023. [2458] 41. Weaver, J. E.; Kramer, Joseph. 1932. Root system of Quercus macrocarpa in relation to the invasion of prairie. Botanical Gazette. 94: 51-85. [274] 42. Welsh, Stanley L. 1986. Quercus (Fragaceae) in the Utah flora. Great Basin Naturalist. 46(1): 107-111. [2498] 43. Welsh, Stanley L.; Atwood, N. Duane; Goodrich, Sherel; Higgins, Larry C., eds. 1987. A Utah flora. Great Basin Naturalist Memoir No. 9. Provo, UT: Brigham Young University. 894 p. [2944] 44. Whitson, Thomas D. 1987. Weeds in Wyoming causing livestock poisoning. In: Fisser, Herbert G., ed. Wyoming shrublands: Proceedings, 16th Wyoming shrub ecology workshop; 1987 May 26-27; Sundance, WY. Laramie, WY: University of Wyoming, Department of Range Management: 55-57. [13922] 45. Williams, Robert D.; Hanks, Sidney H. 1976. Hardwood nurseryman's guide. Agric. Handb. 473. Washington, DC: U.S. Department of Agriculture, Forest Service. 78 p. [4182] 46. Fowells, H. A., compiler. 1965. Silvics of forest trees of the United States. Agric. Handb. 271. Washington, DC: U.S. Department of Agriculture, Forest Service. 762 p. [12442]

Index

Related categories for Species: Quercus macrocarpa | Bur Oak

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Content on this web site is provided for informational purposes only. We accept no responsibility for any loss, injury or inconvenience sustained by any person resulting from information published on this site. We encourage you to verify any critical information with the relevant authorities.

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

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