
Environmental Encyclopedia 3
Forest decline
comprised of an advance regeneration of individuals released
from the understory. Therefore, according to the cohort
senescence theory, the ohia dieback should be considered to
be a characteristic of the natural population dynamics of the
species.
Other forest declines are occurring in areas where the
air is contaminated by various potentially toxic
chemicals
,
and these cases might be triggered by air pollution. In North
America, prominent declines have occurred in ponderosa
pine (Pinus ponderosa), red spruce (Picea rubens) and sugar
maple (Acer saccharum). In western Europe, Norway spruce
(Picea abies) and beech (Fagus sylvatica) have been severely
affected.
The primary cause of the decline of ponderosa pine in
stands along the western slopes of the mountains of southern
California is believed to be the toxic effects of ozone. Pon-
derosa pine is susceptible to the effects of this gas at the
concentrations that are commonly encountered in the declin-
ing stands, and the symptomalogy of damage is fairly clear.
In the other cases of decline noted above that are
putatively related to air pollution, the evidence so far is less
convincing. The recent forest damage in Europe has been
described as a “new” decline syndrome that may in some
way be triggered by stresses associated with air pollution.
Although the symptoms appear to be similar, the “new”
decline is believed to be different from diebacks that are
known to have occurred historically and are believed to have
been natural. The modern decline syndrome was first noted
in fir (Abies alba) in Germany in the early 1970s. In the
early 1980s a larger-scale decline was apparent in Norway
spruce, the most commercially-important species of tree in
the region, and in the mid 1980s decline became apparent
in beech and oak (Quercus spp.).
Decline of this type has been observed in countries
throughout Europe, extending at least to western Russia.
The decline has been most intensively studied in Germany,
which has many severely damaged stands, although a wide-
spread dieback has not yet occurred. Decline symptoms are
variable in the German stands, but in general: (1) mature
stands older than about 60 years tend to be more severely
affected; (2) dominant individuals are relatively vulnerable;
and (3) individuals located at or near the edge of the stand
are more-severely affected, suggesting that a shielding effect
may protect trees in the interior. Interestingly, epiphytic
lichens
often flourish in badly damaged stands, probably
because of a greater availability of light and other resources
caused by the diminished cover of tree foliage. In some
respects this is a paradoxical observation, since lichens are
usually hypersensitive to air pollution, especially toxic gases.
From the information that is available, it appears that
the “new” forest decline in Europe is triggered by a variable
combination of environmental stresses. The weakened trees
588
then decline rapidly, and may die as a result of attack by
secondary agents such as fungal disease or insect attack.
Suggestions of the primary inducing factor include gaseous
air pollutants,
acidification
, toxic metals in soil, nutrient
imbalance, and a natural climatic effect, in particular
drought
. However, there is not yet a consensus as to which
of these interacting factors is the primary trigger that induces
forest decline in Europe, and it is possible that no single
stress will prove to be the primary cause. In fact, there may
be several “different” declines occurring simultaneously in
different areas.
The declines of red spruce and sugar maple in eastern
North America involve species that are long-lived and shade-
tolerant, but shallow-rooted and susceptible to drought. The
modern epidemic of decline in sugar maple began in the
late 1970s and early 1980s, and has been most prominent
in Quebec, Ontario, New York, and parts of New England.
During the late 1980s and early 1990s, the decline appeared
to reverse, and most stands became more healthy. The symp-
toms are similar to those described for an earlier dieback,
and include abnormal coloration, size, shape, and premature
abscission of foliage, death of branches from the top of the
tree downward, reduced productivity, and death of trees.
There is a frequent association with the pathogenic fungus
Armillaria mellea, but this is believed to be a secondary agent
that only attacks weakened trees. Many declining stands had
recently been severely defoliated by the forest tent caterpillar
(Malacosoma disstria), and many stands were tapped each
spring for sap to produce maple sugar. Because the declining
maple stands are located in a region subject to a high rate
of
atmospheric deposition
of acidifying substances, this
has been suggested as a possible predisposing factor, along
with soil acidification and mobilization of available
alumi-
num
. Natural causes associated with
climate
, especially
drought, have also been suggested. However, little is known
about the modern sugar maple decline, apart from the fact
that it occurred extensively; no conclusive statements can
yet be made about its causal factor(s).
The stand-level dieback of red spruce has been most
frequent in high-elevation sites of the northeastern United
States, especially in upstate New York, New England, and
the mid- and southern-Appalachian states. These sites are
variously subject to acidic precipitation (mean annual
pH
about 4.0–4.1), to very acidic fog water (pH as low as 3.2–
3.5), to large depositions of sulfur and nitrogen from the
at-
mosphere
, and to stresses from metal toxicity in acidic soil.
Declines of red spruce are anecdotally known from
the 1870s and 1880s in the same general area where the
modern decline is occurring. Up to one-half of the mature
red spruce in the Adirondacks of New York was lost during
that early episode of dieback, and there was also extensive
damage in New England. As with the European forest de-