Background:
Standing dead trees (snags) are considered
an integral habitat component of cavity?nesting
birds and other wildlife in the coniferous
forests of the southwestern United
States. The species, size, bark retention,
and condition influences the value
of a snag as wildlife habitat. Removal
of snags has been linked to declines
in both diversity and density of cavity-nesting
birds and tree roosting bats in southwestern
forests. Snags also serve as nesting
and perching platforms for numerous
raptor species. Conversions of forests
from old growth to even aged stands
shortens the rotation age from centuries
to decades, thereby reducing the size
and age of the trees left in the forest.
This reduction drastically decreases
the amount, size and quality of dead
and dying trees available for the future.
Currently there are plans to treat
the ponderosa pine forests on Camp
Navajo using restoration prescriptions
that should restore the proper structure
and function of the forest community.
Forest restoration treatments involve
removing accumulated litter and over
stocked stands through burning which
may alter the type and density of snags.
The purpose of this project is to conduct
a survey of snags within the ponderosa
pine forest on Camp Navajo and permanently
mark benchmark snags for future monitoring.
Location:
We inventoried snags throughout the ponderosa
pine forest on the western section of Camp
Navajo Army National Guard Depot. The area
is approximately 10 square miles and is bound
by the western property boundary with the
U.S. Forest Service and the western boundary
of the containment area.
Approach:
We conducted a complete census of snags within
the boundaries measuring snag species composition,
size (height and diameter), decay class and
density. Snags were considered any standing
dead trees greater than 4 inches diameter
at breast height (dbh) and greater than 7
feet tall, with an angle greater than 45
degrees from the ground. Decay classes are
defined as follows: Decay class 1 - snags
that have recently died, typically have little
decay, and retain their bark, branches and
top; Decay class 2 - snags that show some
evidence of decay and have lost some bark
and branches, and often a portion of the
top; and Decay class 3 - snags that have
extensive decay, are missing the bark and
most of the branches and have a broken top.
Decay classes 4 and 5 related to the extent
of the decay on large stumps. We recorded
woodpecker use, beetle infestation and bark
sloughing as a surrogate for bat roost suitability.
Each inventoried snag was marked with a uniquely
numbered aluminum tag and we permanently
marked a representative sample of these for
long term monitoring (approx. 50 each) based
on size class (4-12, 12-18, 18-24, and > 24
inches dbh) and decay class.
Benefits:
An inventory of currently standing snags
will provide biologists with baseline information
about snag density and age prior to implementing
proposed forest restoration treatments. This
study will facilitate the long-term monitoring
of snags to assess decay rates and retention
rates over time. Through monitoring, we will
also gain information about the effects of
forest restoration treatments on snag recruitment.
This information, combined with wildlife
surveys will provide insight to long-term
effects that forest restoration may have
on wildlife species in the ponderosa pine
community.
For more information
contact:
Mylea Bayless, Arizona Game and Fish Department, 5000 W. Carefree Highway Phoenix, AZ 85086-5000
.
Phone: (928) 213-9591 E-mail: mbayless@gf.state.az.us
Michael Ingraldi, Ph.D., Arizona Game and Fish Department, 5000 W. Carefree Highway Phoenix, AZ 85086-5000
.
Phone: (928) 523-5625 E-mail: mingraldi@cybertrails.com
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