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You are here >1Up Info > Wildlife, Animals, and Plants > Plant Species > Tree > Species: Pinus edulis | Colorado Pinyon
 

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FIRE EFFECTS

SPECIES: Pinus edulis | Colorado Pinyon
IMMEDIATE FIRE EFFECT ON PLANT : Pinyons are generally very susceptible to fire mortality [12,40. Tree mortality, however, is largely determined by the extent to which trees dominate a site. Where pinyon trees have recently invaded grassland communities, young trees less than 4 feet (1.2 m) tall are easily killed. As tree dominance increases and the understory is gradually suppressed, the ability of the understory to carry fires intense enough to kill larger trees also decreases [57]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Colorado pinyons reestablish from seed cached by rodents and birds after fire. Reentry into the plant community depends upon perennial nurse plants associated with mid-successional and late-successional stages. Although trees become established 20 to 30 years after burning, coverages and densites are relatively low until approximately 60 years after fire, at which time tree dominance begins to exceed that of the understory. Pinyons dominate a site within 100 to 150 years of burning [30,56]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : Since pinyons usually require protected sites near the base of 1- to 2-foot-tall (0.3-0.6 m) shrubs for successful establishment, pinyons can be expected to reestablish sooner on sites where mid to late seral stages existed prior to burning. Pinyons begin to dominate sites very early in the sere, usually when trees are only 3 to 6.5 feet (1-2 m) tall. As tree roots grow into moisture supplies, understory species decline at an increasingly rapid rate. Areas converted to grasslands should be burned every 20 to 40 years depending on the rate of pinyon reinvasion [57]. FIRE MANAGEMENT CONSIDERATIONS : Prescribed fire is no longer an effective managment tool on many pinyon-juniper sites where prolonged tree dominance has not only reduced the ability of the understory to carry fires but has also seriously lowered the ability of the understory to respond to fire. When fires do occur in closed stands, intensities are often so severe and the soil seed reserves so depleted, that without successful seeding, highly flammable annual grass communities are often established [13,54]. On many overgrazed woodlands, seeding burns is the only way to restore a desirable perennial grass stage. Prescribed fire can be used on some sites, depending on stand structure and understory composition. In open stands with 700 to 1,000 pounds per acre (786-1,123 kg/ha) of fine fuels, low-intensity spring fires are very effective in eliminating pinyon less than 4 feet (1.2 m) tall. Mortality of taller trees in open stands is relatively low unless fuels have accumulated around tree bases (12,57]. Optimal burning conditions in open stands are: air temperatures of 70 to 74 degrees Fahrenheit (21-23 deg C); relative humidiy of 20 to 40 percent; and wind speed of 10 to 20 mph (16-32 km/h). Closed stands with little understory are extremely difficult to burn and carry fires only on hot summer days when burning conditions are often hazardous: air temperatures of 95 to 100 degrees Fahrenheit (35-38 deg C); low relative humidity; and wind speed of 8 to 20 miles per hour (13-32 kmh). Burning under these conditions usually results in extremely intense crown fires. Fires carry better as tree density increases and as the proportion of pinyon to juniper within a stand increases. This increased ease of burning has been attributed to both the greater flammability of pinyon and the increased site potential associated with pinyon-dominated stands [7]. In the Great Basin woodlands, the best candidates for effective prescribed burning are ecotonal areas where trees have invaded sagebrush-grassland communities; sites usually have a shrub and tree cover ranging from 45 to 60 percent [8]. These sites can be burned effectively with low-intensity spring burns which eliminate the tree overstory; in most cases, reseeding is not required for adequate postfire understory response [13].

Related categories for Species: Pinus edulis | Colorado Pinyon

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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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