Bonanza Creek LTER
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Disturbance and the taiga ecosystem

Fire

Most forest communities in interior Alaska have been extensively influenced by recurring fire. Because interior Alaska tree species have thin bark, even light fires generally result in extensive tree mortality.

Active Fire in the taiga, Manley Fire, 1969. from Naturalist 25 (Special Issue #1), 1974. Photo by Leslie A. Viereck, USDA FS.

Most forest communities in interior Alaska have been extensively influenced by recurring fire. Because interior Alaska tree species have thin bark, even light fires generally result in extensive tree mortality.

In spite of the lack of detailed data on fire periodicity in Alaska, several researchers have estimated the length of the fire cycle in interior Alaska. Viereck and Schandelmeier (1980) estimated that the natural fire cycle for the Alaska taiga ranges from 50-200 years. Rowe et al. (1974) estimated the following fire cycles for the Mackenzie Valley of Canada: 80-90 years for the black spruce type, 30-70 years for the jack pine type, and 300 years for white spruce stands on alluvial sites. For the Alaska taiga, Heinselman (1978) estimated the fire cycle to be 130 years for open spruce-lichen forest and 100 years for closed black spruce. Yarie (1981) reported a fire cycle of 59.1 years for white spruce, 58.9 years for black spruce, and only 28.6 years for deciduous tree stands in the Porcupine River drainage.

Many plants in the Alaska taiga are well adapted to reproducing themselves after fire. Although black spruce is not fire-resistant, it is adapted to fire through its semiserotinous cones. Branches close to the ground, shallow roots, thin bark, and abundant lichens on lower branches combine to make black spruce especially vulnerable to death from fire. Cones high in the crown are generally not consumed, and they retain viable seeds after the fire even though the trees are dead. Birch and aspen are also well adapted to recurring fires, both species vigorously reproducing vegetatively following fire. Additionally both species are prolific producers of light seed which can be disseminated long distances by the wind.

Flooding and Other Fluvial Processes

The heavy sediment load of the glacier-fed Tanana River supports an aggrading system where silt deposition associated with floods builds terraces of increasing height on the active floodplain. These fluvial processes, including erosion and silt bar formation, shape the surfaces on which ecosystem processes take place.

Click to enlarge. Aerial view of downtown Fairbanks near crest of flood on Chena River, August 15, 1967. Arrow indicates direction of flow of river. from US Geological Survey, Flood of August 1967 at Fairbanks, Alaska. Photograph by the Alaska Railroad.

Insect Outbreaks
Insect outbreaks are extensive only in more continental regions of southern Alaska, where the climate is relatively warm. Here insects have eliminated spruce forests over broad areas, leading to extensive areas of grasslands. High population levels of spruce budworm (Choristoneura fumiferana, C. orae) were first observed in BNZ in 1989. Repeated defoliation in 1991 and 1992 caused top-kill in trees and mortality in seedlings and saplings. Outbreaks of bark beetles also caused significant mortality in 1993. A new disturbance study of simulated bark beetle outbreak has been initiated at BCEF.

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The Bonanza Creek LTER, including this website, is supported by the National Science Foundation through awards DEB-0620579, DEB-0423442, DEB-0080609, DEB-9810217, DEB-9211769, DEB-8702629 and by the USDA Forest Service, Pacific Northwest Research Station through agreement number RJVA-PNW-01-JV-11261952-231. Any opinions, findings, conclusions, or recommendations expressed in the material are those of the author(s) and do not necessarily reflect the views of the supporting agencies or the program as a whole.

© Bonanza Creek LTER, 2008.
Last modified 19-Aug-08

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