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October
1991
Woodland
Fish and Wildlife
Managing Small Woodlands
for Cavity Nesting Birds
Dead trees or
snags provide a valuable forest component for wildlife which use these standing
habitats as a place to feed, nest, perch and roost. Some birds which inhabit
tree cavities feed on insects, which left uncontrolled, can cause damage to
commercial crop trees. As cavity trees decay, they eventually fall and become
large woody material on the forest floor, providing additional benefits for
wildlife as well as improving soil productivity.
Some small
mammals, birds and amphibians use large, down woody material as a place to live
and feed on insects, seeds and fungi found on the forest floor. Forest managers
know that if soil fungi is eliminated from the forest system, tree seedlings
have difficulty becoming established because they cannot successfully extract
nutrients and minerals from the soil. Small mammals feed on fungi and pass
fungal spores in their droppings. As the animals move about the forest they
dispense spores and insure that the invaluable fungi will remain available
throughout forest succession.

| Figure
1. When they fall, trees and snags immediately enter one of the first
four log decomposition classes (reproduced from Maser et al. 1979, p.
80) |
|

|
Snag Type 3 -
Live defective trees that are safe for topping to reduce susceptibility to blowdown
after harvest.
|
|
As large woody
material decays over time it continues to provide benefits for a woodlot and the
ecosystem. Decaying wood acts as a reservoir for water storage by slowly
releasing moisture throughout the summer. This helps maintain a moist, cool
forest floor where seedlings can survive. Phosphorus, potassium and other
nutrients are released providing essential elements for the growth of trees.
Nitrogen fixing bacteria live in decaying wood and produce nitrogen, an
essential nutrient for forest tree growth. Eventually, over a period of years,
the decaying woody material becomes part of the soil, contributing to the cycle
of forest health.
DEAD TREE
HABITATS
West of the Cascades in Oregon and Washington, 39 species of birds and 14
species of mammals depend on cavity trees for their survival. East of the
Cascades 39 bird species and 23 mammal species depend on these trees.
Additionally, many species of fungi, moss, lichens, ferns, invertebrates,
reptiles and amphibians that form an integral part of a healthy forest also
depend on dead trees and down woody material for all or a part of their life
cycle.
Habitat for
cavity dwelling birds begins to form when a large tree dies and forms a
"HARD SNAG" with the bark still intact and with firm heart and
sapwoods. Later, this hard snag decays to become a "SOFT SNAG" which
may have some bark remaining but with the wood beginning to soften. As
decomposition continues, a soft snag may become a "BUCKSKIN SNAG"
where the bark is missing and the wood continues to soften. Decomposition causes
snags to become shorter and shorter as parts of the top decay and successively
fall, adding woody material to the forest floor. Each of these progressive
changes in a cavity tree represents a structural habitat change that benefits a
different group of birds. Snags may provide habitat over a period of 30 to 70
years depending on the size and species of tree and the type of forest in which
it occurs.
A recently dead
tree or hard snag is first used by woodpeckers, called primary excavators, which
are capable of making a cavity in wood. Woodpeckers that may use hard snags
include:
After the hard
snag decays and softens, a different group of primary excavators move in and
create cavities. Three species of chickadees, the Lewis' woodpecker and three
species of nuthatches are examples. These cavities are later used by about 27
bird and 18 mammal species that can't make their own cavities, but rely on
cavities made and abandoned by woodpeckers. This group is called the
"secondary cavity user" group. Some examples are:
-
mountain
bluebird
-
western
bluebird
-
house
wren
-
tree
swallow
-
wood
duck
-
goldeneye
duck
-
barn
owl
-
pygmy
owl
-
saw-whet
owl
-
American
kestrel
-
Vaux's
swift
-
bats
-
squirrels
-
marten
-
raccoon
-
porcupine
An additional
25 bird and 23 mammal species depend on tree cavities during some time of the
year if they are to survive in timbered areas.
In addition to
the benefits that cavity dependent birds provide in consuming insects, some
species such as owls, kestrels, weasels and marten prey on gophers, voles, hares
and mountain beaver which may cause significant losses in young forest stands.
CAVITY TREE
MANAGEMENT
Trees managed for cavity nesters should meet minimum height and diameter
criteria and occur in the woodlot in specific places in relation to riparian
zones, slope position and aspect. The number of existing cavity trees and the
number of "replacement" cavity trees is important in maintaining long
term populations of cavity dependent birds. A minimum number of cavity trees
would be two "hard', one "soft" and three "replacement"
green (live) trees per acre with a minimum diameter of 15 to 17 inches and a
height of 15 to 30 feet.- In a dear cut larger than 10 acres, a minimum number
of cavity trees would be two snags or two green trees at least 30 feet in height
and 11 inches DBH at least 50 percent of which are conifers. Additionally, two
downed logs or trees, 50 percent of which are conifers, that are at least 12
inches in diameter and 16 feet long, should be left for wildlife. If trees of
this size are not available, equivalent volume of downed material will suffice.
A snag tree that is 20-24 inches in diameter and at least 30' high will provide
habitat for large species like the pileated wood pecker and wood duck as well as
the smaller species. These cavity trees should be distributed over 50 to 75
percent of the woodlot. Green replacement trees are as important as existing
snags in a healthy forest because they replace snags that fall over, ensuring a
constant supply of snags through time.
The most
productive cavity habitat will be present when a variety of trees species,
diameters and heights are available throughout the woodlot. Conifers usually
last longer than other species. In general, cavity trees less than 12 inches in
diameter and less than 15 feet high provide the least amount of benefits. Also
your woodlot should have a minimum of two pieces of large, downed woody material
per acre in various stages of decay. These pieces should be 10 feet long to be
most effective in maintaining wildlife habitat and forest health.

| 'Wildlife
trees may be left where they will cause little problem if they fall,
such as along roads so they do not threaten to roll, fall or slide into
the right-of-way. |
Tree species
which provide good quality cavity habitats vary depending on the type of
vegetative community they are in. Grand fir, Douglas fir, ponderosa pine,
spruce, larch, western red cedar, cottonwood and willow are used because they
tend to stand for long periods of time. The best hardwoods to grow on a woodlot
to provide cavities are big leaf maple, oak and alder. The type of habitat in
which a snag is located will also determine which wildlife use it. A snag in a
young forest will provide habitat for a different set of species than a snag in
an old stand.
Large cavity
trees will usually stand longer than small diameter trees and could be present
through many stages of forest development. Small diameter cavity trees provide
minimum opportunity for cavity dependent birds and deteriorate within a few
years. Where conditions permit, cavity trees should be located within riparian
zones or wet areas, along the upper one third of slopes, and on the south and
east slopes. Cavity trees in riparian zones eventually fall and may add large
woody debris to stream channels. This is a valuable component for maintaining
pools and riffles which provide fish habitat, aquatic insect habitat and
protection for fish from predators.
If the woodlot
has no cavity trees present, potential future cavity trees can be selected from
diseased live trees, possibly with heart rot or a dead top. Live trees without
such problems, but not suitable for market, can be purposely injured to create
snags. Tops can be removed from live trees or they can be partially barked.
These practices imitate nature by providing a place for organisms and fungi to
enter the tree and begin the decay process. Burning will also kill trees, but
often "case hardens" the snag rendering it less valuable to wildlife.
Trees killed by fire should be left, however, because they provide structure and
perch sites in the forest. Live trees may be left during harvest to grow to the
diameter and height needed for good cavity trees. Scheduling future cavity trees
in "time and space" assures the manager of a constant supply of birds,
mammals and large woody debris.
SAFETY
Cavity trees can be a hazard to vehicles, buildings, power lines, fences and
workers if not managed properly. Cavity trees should be located where they will
not damage property or cause injury if they fall. Plan and organize work to
prevent workers and equipment being in the "fall zone" of cavity
trees. Guidelines for safe cavity tree nesting management are available from
various state and federal agencies.

| "Wildlife
trees can be left along lakes, ponds or streams, especially where the
lean is over water or along the edge away from work area." |
|
CHECKLIST FOR
CAVITY
TREE MANAGEMENT
Use this
checklist to evaluate the health of your woodlot. Cavity trees
and replacement trees should be a minimum of 15 to 17 inches DBH
and 15-30 feet tall.
|
|
GOOD |
NEEDS
HELP |
Hard
Cavity Trees:
Less than 1/acre |
|
yes |
Soft
Cavity Trees:
Less than 1/acre
1 or more/acre |
.
yes |
yes
. |
Future
Cavity Trees:
Less than 1/acre
1 or more/acre |
yes |
yes
|
Distribution
over woodlot:
less than 25%
25% to 49%
50% to 74%
more than 75% |
.
.
.
yes
(very good) |
.
yes
yes |
| . |
|
|
| Down
Woody Debris (two pieces per acre in each decay class 16 feet
long by 20 inches in diameter.) |
| . |
|
|
| . |
2
OR MORE |
LESS
THAN 2 |
| Class 1
sound |
yes |
no |
Class 2
soft
(contact w/ground) |
yes |
no |
Class 3
soft
(partially buried) |
yes |
no |
| Class 4
skeleton remains |
yes |
no |
|
REFERENCES
1979. Wildlife
Habitats in Managed Forests the Blue Mountains of Oregon and Washington. Ag.
Handbook No. 553. J.W. Thomas, Ed. USDA, Forest Service, Pacific NW Region,
Portland, OR. 511 PP.
1985.
Management of Wildlife and Fish Habitats in Forests of Western Oregon and
Washington. E. Reade Brown, Tech. Ed. USDA, Forest Service, Pacific NW Region,
Portland, OR. Pub. No. R-6F&WL-192-1985. Two Vol. 634 pp
1986. Guideline
for Selecting Live or Dead Standing Tree Wildlife Habitat. Pub. No.
R6-F&WL-219-1986. USDA Forest Service, Pacific NW Region, Portland, OR. 9
PP.
Available from Fish and Wildlife Division, US Forest Service, P.O. Box 3623,
Portland, OR. 97208
OUR PURPOSE
This leaflet was written by Richard J. Pederson, Wildlife/Silviculturist
Program Manager, U.S.D.A. Forest Service Pacific Northwest Region.
The
Woodland Fish and Wildlife Project is a cooperative effort among the World
Forestry Center, Oregon State Department of Forestry, Washington State
Department of Natural Resources, Oregon State University Extension Service,
Washington State University Cooperative Extension, University of Washington
Center of Streamside Studies, Oregon Association of Conservation Districts,
Oregon Small Woodlands Association, Washington Farm Forestry Association, Oregon
Department of Fish and Wildlife, Washington Department of Fisheries, Washington
Department of Wildlife, Oregon Soil Conservation Service, Washington Soil
Conservation Service and the USDA Forest Service. The World Forestry Center
serves as the coordinating organization for the project.
The
Woodland Fish and Wildlife Project was initiated to provide information on fish
and wildlife management to private woodland owners and managers. It is the
intent of the organizations involved in this project to produce publications
that will serve as practical guides to woodland owners. Each publication is
intended to be complete in itself. Users may find it convenient to collect all
publications in this series in a three ring binder to form a permanent reference
file. Woodland Fish and Wildlife Project publications range from an overview of
fish and wildlife opportunities on woodland properties to specific publications
concerning techniques for managing individual species.
These
publications can be obtained from any of the cooperating organizations or by
contacting the World Forestry Center, 4033 SW Canyon Road, Portland, OR 97221,
(503)228-1367.
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