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You are here >1Up Info > Wildlife, Animals, and Plants > Plant Species > Tree > Species: Pinus resinosa | Red Pine
 

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FIRE EFFECTS

SPECIES: Pinus resinosa | Red Pine
IMMEDIATE FIRE EFFECT ON PLANT : Thick bark allows mature red pine (50 years old or 50 feet tall) to survive relatively intense surface fires. Red pine are killed by crown fires or by surface fires that result in considerable crown scorch [33]. Moderate-intensity surface fires (<200 Btu/s/ft [<692 kW/m]) do not scorch the crowns of mature red pine. A large red pine may survive a surface fire intensity of 500 Btu/s/ft (1,730 kW/m), but this intensity is probably the highest red pine can withstand [40]. In a study in New England, many red pines less than 4 inches (10 cm) survived their first surface fire [10]. Two stands, in which 96 percent of the red and white pines were 9 inches (23 cm) in diameter or larger, were prescribed burned in late spring (May 31 and June 15). The percent crown scorch was estimated after the fire, and 1 year later mortality was assessed. There was no mortality in trees with less than 46 percent crown scorch. Mortality was 50 percent in the 81 to 85 percent crown scorch class and 100 percent in trees with more than 96 percent crown scorch [27]. An April surface fire in a 47-year-old red pine plantation in Minnesota resulted in less mortality than the abovementioned study. The red pine were 50 to 60 feet (15.2-18.3 m) tall, and most trees were between 6 and 11 inches (15-28 cm) in d.b.h. One and a half years after the fire, mortality was 40 percent in the 95 to 100 percent crown scorch class, 14 percent in the 75 to 95 percent crown scorch class, and 8 percent or less in those pines with less than 75 percent crown scorch. The fire took place while the new shoots were still in the terminal buds. Mortality would probably have been higher if the fire had occurred after the buds had opened but before the next year's buds had formed [36]. A laboratory study in August, in which red pine seedlings were exposed to different temperature regimes for 4 minutes, demonstrated even less mortality with high percentages of needle scorch. The seedlings withstood up to 90 percent needle scorch with only 10 to 20 percent mortality. The author suggests that there may be two lethal temperatures, one that kills needles and one that kills terminal buds. Therefore, percent needle scorch may not be directly related to mortality in red pine [27]. A completely developed seed may survive in a cone in the crown after a surface fire that completely killed the crown foliage, but an undeveloped seed is unlikely to complete its development under these conditions [40]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : In natural red pine stands, crown fires are rare because stands are open. However, dense plantation stands up to 50 feet (15.2 m) tall are at high risk of intense crown fire. Red pine is highly flammable and crown fires can reach intensities up to 6,500 BTU/s/ft (22,500 kW/m) [40]. PLANT RESPONSE TO FIRE : Fire provides red pine with conditions necessary for regeneration, specifically a bare or lightly covered mineral seedbed free of brushy competition and an open canopy. A summer surface fire averaging 200 to 500 Btu/s/ft (692-1,730 kW/m) with small scale variations in intensity to ensure the survival of some seed trees is ideal for regeneration [40]. However, not all canopy-opening fires result in red pine recruitment because good seed crops are infrequent [10]. Red pine establishment is sometimes delayed for up to 10 years after a fire [3]. In one study, seedling counts at postfire year 1 correlated positively with fire severity, exposure of mineral soil, and reduction of shrub weight per acre [39]. A thick organic layer is an unfavorable seedbed because germinants are farther from a constant water supply and the mineral soil. The higher the fire severity, the more organic material is removed. However, fire also consumes seeds and rhizomes and thus reduces the early postfire herbaceous cover which serves to shelter the young seedlings from heat. Initially, as the amount of postfire shelter is reduced by increasing fire severity, red pine survival decreases. Eventually, however, the reduction in organic matter depth is sufficient to compensate for the lack of shelter, and the survival of red pine increases. Establishment is highest when mineral soil is exposed [37]. A study of slash pine (Pinus elliottii) showed that if the crown is partially scorched, a loss in growth can be expected, possibly as much as 1 year's growth in the first 2 postfire years. The author believes these results are applicable to red pine [15]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : Prescribed fire is used for red pine site preparation. In the shelterwood system, two fires conducted in consecutive years are recommended before the first partial cut. A fire conducted after the partial cut may be too hot because of slash and may cause mortality of the remaining trees. The first fire should be in the spring before understory leaves emerge so that the fire will be hot enough to remove most of the soil surface organic material [41]. Sufficient duff is removed only when the moisture content is less than or equal to 60 percent [40]. A second fire after the leaves emerge helps reduce competition. A suggested reasonable fire intensity for preparing a seedbed and controlling competition is 116 to 173 Btu/s/ft (400-600 kW/m) [41]. Van Wagner [40] states that 200 Btu/s/ft (692 kW/m) is the upper limit of intensity to avoid crown scorch in 70- to 80-foot (21-24 m) red pine. This intensity is lower than is ideal for natural regeneration because trees do not need to be killed to open up the canopy in a shelterwood system. Two consecutive annual fires in a 90-year-old red and white pine stand in Ontario improved the initial conditions necessary for pine regeneration. The fires were low in intensity (22 to 23 Btu/s/ft [78-79 kW/m]) and did not harm the overstory. The litter layer was consumed and the understory was changed from one dominated by balsam fir saplings to one dominated by herbaceous species. However, the understory will revert back to prefire conditions unless some of the canopy is removed in a shelterwood cut [28]. The red pine cone beetle, and possibly the red pine cone moth, can be controlled by prescribed fire. Adults overwinter on the forest floor and are vulnerable to low-severity ground fires from late October to early May. Because the decrease in the red pine cone beetle might result in an increase in other pests, such as the red pine coneworm, the prescribed burning treatment should be limited to years with heavy cone production [29]. Equations have been developed to predict the forest floor fuel weight and the litter weight in red pine stands from the basal area [9].

Related categories for Species: Pinus resinosa | Red Pine

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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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