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Bob
Campbell is Ecologist and Botany and Rare Plant Program Manager
for the Fishlake National Forest in Richfield, UT. He began his
32-year Forest Service career with the Intermountain Research Station’s
Aspen Ecosystem Unit and worked in Logan from 1974 to 1984. He worked
at the Forestry Sciences Lab in Missoula and earned an M.S. in Forestry
from the University of Montana prior to moving to Richfield in 1993.
Bob’s recent work focuses on watershed assessments, restoration
of aspen and other ecosystems, interagency rare plant programs,
and invasive species management. |
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Abstract:
Aspen Restoration Efforts on the Fishlake National Forest: Lessons
Learned
Henningson, Allen V.,
USDA-FS Fishlake NF, Richfield, UT, Robert B. Campbell, Jr.,
USDA-FS Fishlake NF, Richfield, UT, and Dale L. Bartos, USDA-FS
Rocky Mountain Research Station, Forestry Sciences Lab, Logan, UT.
More than 30 different
areas with aspen, totaling at least 20,000 acres, have been treated
on lands administered by the Fishlake National Forest during the
past 25 years. Aspen harvests, conifer harvests, prescribed burns,
combinations of these treatments, wildland fire use, and wildfire
have all resulted in vigorous stands of young aspen. Examples of
these treatments will be shown and discussed. Some of these areas
had stable aspen stands; other areas had decadent aspen where the
stands were falling apart. However, most of the treated areas were
successional to conifers and included a component of Engelmann spruce,
sub-alpine fir and/or Douglas-fir.
Many of these areas show
excellent, or acceptable, success for aspen regeneration. However,
responses have been mixed; not all have done well, and others essentially
do not have any aspen regeneration remaining in the treated area.
Several lessons can be learned from these treatments on the Fishlake
N.F. Aspen will respond to a variety of treatments done during every
season of the year. It is rare that a stand with aspen present would
not produce suckers, usually abundant, if the hormonal response
is stimulated. Protection may be necessary for young aspen suckers
to establish and thrive. Many areas have been fenced; some have
high fences to exclude wildlife while other fences exclude only
livestock. However, the fences may have been installed too late
in a few cases. There is value in using three-way exclosures to
help determine the kind of use. Treatments can be modified to enhance
environmental conditions for optimum sucker production. We recommend
that only a part of the clone or area be treated at one time; do
nothing in the remaining portion. Use fire as an element of the
treatment if advanced conifer regeneration is abundant and likely
to compromise successful aspen regeneration. Priority should be
given to treating areas that are successional to conifers.
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