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You are here >1Up Info > Wildlife, Animals, and Plants > Kuchler Potential Natural Vegetation Type > Northern Floodplain Forest
 

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KUCHLER TYPE FIRE ECOLOGY AND MANAGEMENT

KUCHLER TYPE: Northern floodplain forest
FUELS, FLAMMABILITY, AND FIRE OCCURRENCE : Fire is rare in northern floodplain forest in humid climates. Higgins [21] noted that fire was frequent enough to favor grasslands in the northern Great Plains, but that areas with rough and dissected topography were much less likely to experience fire [21]. However, occasionally fire probably influenced presettlement northern floodplain forests in drier climates. In a North Dakota gallery forest, the oldest trees were only 80 years old, even though the forest had been recorded in presettlement survey records. A long-term local resident noted that prairie fires frequently invaded the forest and sometimes killed some of the larger trees [27]. FIRE EFFECTS ON SITE : NO-ENTRY FIRE EFFECTS ON VEGETATION : Willows (including black willow, sandbar willow, and peachleaf willow) are usually top-killed by fire. Severe fire that consumes organic layers and exposes roots kills most willows. Most top-killed willows sprout following fire; however, black willow typically decreases following fire [57]. Willows are pioneer species on burned sites and establish from light, windborne seed [54]. Fire easily kills cottonwood seedlings and saplings. Trees less than 20 years old may sprout after fire damage. Large cottonwoods have thick bark which may provide some resistance to fire damage, but fire wounds are likely to create avenues for infection [58]. Mid- and late successional northern floodplain species such as American elm, silver maple, and boxelder are easily damaged or killed by fire, particularly when young. Some species sprout after damage or top-kill, particularly green ash [16]. Bur oak is more resistant to fire damage; prairie fires burning into bur oak-dominated stands tend to maintain the large oaks with a grassy understory [42]. Controversy continues over whether northern Great Plains woodlands have expanded or declined since settlement and the beginning of fire exclusion in the late 19th century. The suppression of fire may have allowed woodland expansion; but some authors argue that woodland species are adapted to fire (due to sprouting ability and rapid colonization of bare sites) and thus may be limited by climate and moisture availability [58]. In the absence of fire, trees and shrubs may replace prairie grasses on mesic sites [51]. FIRE EFFECTS ON RESOURCE MANAGEMENT : NO-ENTRY FIRE USE CONSIDERATIONS : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : Myers and Buchman [37] do not consider fire a management tool for site preparation or shrub control in elm-ash-cottonwood types. All species present are susceptible to fire damage; surface fire readily kills saplings and seedlings, and wounds larger trees. Fire wounds lead to heart rots and decrease timber values [37]. Putnam [41] also made a general recommendation against the use of prescribed fire for any objectives in bottomland forests. REHABILITATION OF SITES FOLLOWING WILDFIRE : NO-ENTRY

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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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