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You are here >1Up Info > Wildlife, Animals, and Plants > Plant Species > Tree > Species: Picea rubens | Red Spruce
 

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FIRE EFFECTS

SPECIES: Picea rubens | Red Spruce
IMMEDIATE FIRE EFFECT ON PLANT : Red spruce is easily killed by fire [49]. Surface or ground fires that consume the litter and organic layers covering the superficial roots of red spruce are almost certain to severely injure the roots [39]. Fire kills mature trees by exposing roots, subjecting the tree to water stress and/or windthrow, which may result in the eventual death of the tree [39,87]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Red spruce does not sprout. Seed germination is greater on burned areas with exposed mineral soil than in duff; mortality, however, is also greater due to increased surface temperature and drought [63]. Burned red spruce or spruce-fir stands are initially restocked by aspen (Populus spp.) or birch (Betula spp.) via wind-disseminated seed; paper birch (Betula papyrifera)-aspen stands are particularly diagnostic of fire in upland red spruce forests [52]. Red spruce seedlings appear a few years after fire, developing as an understory in the aspen-birch complex, and eventually penetrate the overstory after 50 or 60 years. Birch and aspen become decadent after 75 to 80 years and red spruce or red spruce and balsam fir regain dominance if left undisturbed [49,52,65]. On better sites, northern hardwoods, chiefly sugar maple and American beech, may replace red spruce, and in some areas, balsam fir will dominate the late postfire succession. Postharvest/postfire restocking by red spruce is extremely slow where the organic layers are destroyed by severe fire (particularly where harvest has been heavy) [49]. In Nova Scotia, mature spruce forests have few herbs and shrubs in the understory. After a fire, herbs increase in the first 6 years and dominate for 40 or more years while conifers slowly establish [54]. After fire in the southern Appalachians, blackberry (Rubus ursinus) and red raspberry colonize the site. Pin cherry and yellow birch follow. Blackberry and raspberry are too competitive for red spruce and must be shaded out by the hardwoods before red spruce can establish [39]. In West Virginia, postlogging and postfire succession in red spruce forests follows a similar pattern: ferns and raspberry are followed by other shrubs, then hardwoods (particularly hawthorn [Crataegus spp.]), and eventually spruce. In many areas, this successional pattern has been extremely slow; heaths or barrens form that do not appear as if they will ever return to forest [13]. Martin [54] studied postlogging/postfire succession in Nova Scotia and found that red spruce was present on most sites after the second postfire year, becoming more numerous and dominant in the later seres. He concluded that repeated heavy cuttings and light fires on the poorer soils of the southern upland of Nova Scotia encourages the invasion of heath plants, which limits the rate and amount of tree regeneration. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : Some managers believe that prescribed fire may be a useful silvicultural tool for managing red spruce on some sites. On such sites, the exposed mineral soil must have plentiful moisture, soil temperatures must be moderate, and competition must be minimal [65]. In general, however, fires in red spruce habitat are of little silvicultural value [87]. Slash burning following logging kills advance reproduction and creates rank postfire vegetation that delays any new seedling establishment [39]. The fire management plan for Acadia National Park, Maine, dictates the suppression of natural fires. Prescribed fires may be used on occasion to reduce fuels [61]. Patterson and others [60] estimated fuel loadings for a number of stands in Acadia National Park that contained red spruce. They concluded that fire exclusion was probably resulting in increased fuel loads. Alexander [4] compiled slash fuel indices for red spruce and compared actual fire spread, intensity, and slash and organic layer depletions with those predicted by the Canadian Forest Fire Danger Rating System. Freeman and others [24] developed equations to determine average crown weight per tree as a function of tree height and diameter for use in a method to predict slash weight after logging red spruce.

Related categories for Species: Picea rubens | Red Spruce

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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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