
Environmental Encyclopedia 3
Old-growth forest
logical and regulatory purposes. The task was complicated
by the great diversity in forest types, as well as by different
views of the purpose and use of the definition. For example,
60 years of age might be considered old for one type, whereas
200 or 1,000 years might be more accurate for other types.
Moreover, forest attributes other than age are more impor-
tant for the wellbeing of certain
species
which are dependent
on forests commonly considered old growth, such as the
northern spotted owl
and marbled murrelet. Nonetheless,
some common attributes and criteria were developed.
Old-growth forests are now defined as those in a late
seral stage of ecological succession, based on their composi-
tion, structure, and function. Composition is the representa-
tion of plant species—trees, shrubs, forbs, and grasses—that
comprise the forest. (Often, in referring to an old-growth
stand foresters limit composition to the tree species present).
Structure includes the concentration, age, size, and arrange-
ment of living plants, standing dead trees (called “snags"),
fallen logs, forest-floor litter, and stream debris. Function
refers to the forest’s broad ecological roles, such as
habitat
for terrestrial and aquatic organisms, a repository for genetic
material, a component in the hydrologic and biogeochemical
cycles, and a climatic
buffer
. Each of these factors vary and
must be defined and evaluated for each forest type in the
various physiographic regions, while accounting for differ-
ences in disturbance history, such as wildfires, landslides,
hurricanes, and human activities. The problem of specifically
defining and determining use of these lands is exceedingly
complex, especially for managers of multiple-use public lands
who often are squeezed between the opposing pressures of
commercial interests, such as the timber industry, and envi-
ronmental preservation groups. The modern controversy
centers primarily around forests in the northwest of United
States and Canada—forests consisting of virgin
redwoods
,
Douglas firs, and mixed conifers.
As an example of old-growth characteristics, the
Douglas-fir forests are characterized by large, old, live trees,
many more than 150 feet (46 m) tall, 4 ft (1.2 m) in diameter,
and 200 years old. Interspersed among the trees are snags
of various sizes—skeletons of trees long dead, now home to
birds, small climbing mammals, and insects. Below the giants
are one or more layers of understory—subdominant and
lower growing trees of the same or perhaps different species,
and beneath them are shrubs, either in a thick tangle provid-
ing dense cover and blocking passage or separated and
allowing easy passage. The trees are not all healthy and
vigorous. Some are malformed, with broken tops or multiple
trunks, and infected by fungal rots whose conks protrude
through the bark. Eventually, these will fall, joining others
that fell decades or centuries ago, making a criss-cross pattern
of rotting logs on the forest floor. In places, high in the
trees, neighboring crowns touch all around, permanently
1027
shading the ground; elsewhere, gaps in the canopy allow
sunlight to reach the forest floor.
Proponents of harvesting mature trees in old-growth
forests assert that the forests cannot be preserved, that they
have reached the
carrying capacity
of the site and the stage
of decadence and declining productivity that ultimately will
result in loss of the forests as well as their high commercial
value which supports local lumber-based economies. They
feel that society would be better served by converting these
aged, slow-growing ecosystems to healthy, productive, man-
aged forests. Management proponents also argue that ade-
quate old-growth forests are permanently protected in desig-
nated wildernesses and national and state parks. Moreover,
they point out that even though most old-growth forests are
on
public land
, many forests are privately owned, and that
land owners not only pay taxes on the forests, but they also
have made an investment from which they are entitled a
reasonable profit. If the forests are to be preserved, land
owners and others suffering loss from the preservation should
be reimbursed.
Proponents of saving the large old trees and their
environments claim that the forests are dynamic, that al-
though the largest, oldest trees will die and rot, they also
will be returned to earth to support new growth, foster
biological diversity, and preserve genetic linkages. Moreover,
protection of the forests will help ensure survival of depen-
dent species, some of which are threatened or endangered.
Defenders claim that the trees will not be wasted; they simply
will have alternative value. They believe that their cause is
one of moral as well as biological imperative. More than 90%
of America’s old-growth forests have been logged, depriving
future generations
of the scientific, social, and psychic
benefits of these forests. As a vestige of North American
heritage, the remaining forests, they believe, should be ma-
nipulated only insofar as necessary to protect their integrity
and minimize threats of natural fire or disease from spreading
to surrounding lands. See also American Forestry Associa-
tion; Endangered species; National forest; National Forest
Management Act; Restoration ecology
[Ronald D. Taskey]
R
ESOURCES
B
OOKS
Arrandale, T. The Battle for Natural Resources. Washington, DC: Congres-
sional Quarterly, Inc., 1983.
Kaufmann, M. R., W. H. Moir, and R. L. Bassett. Old-Growth Forests in
the Southwest and Rocky Mountain Regions. Proceedings of a Workshop.
Washington, DC: U.S. Forest Service, Rocky Mountain Forest and Range
Experiment Station, 1992.
O
THER
Spies, T. A., and J. F. Franklin. “The Structure of Natural Young, Mature,
and Old-Growth Douglas-Fir Forests in Oregon and Washington.” In