4. Forest Issues and Trends
4.1 Environmental Issues in Forestry
4.1.1 Forest Decline
New Types of Forest Damage and Countermeasures
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Air pollution is one of the primar damage factor for our forests; an important
part is played by
sulphur dioxide which comes from power and heating plants, industry and
household burners.
Nitrogen oxides which emanate largely from the exhaust pipes of our cars,
cause damage to
vegetation, too. Together with hydrocarbons and under the influence of
the suns energy, they are
converted into photooxidants, e.g. ozone. Photooxidants are strongly poisonous
to plants and cells.
They presumably play a substantial part in the damage done to the higher
mountain forests.
In addition there are other air pollutants like heavy metals (e.g. lead),
hydrocarbons, fluorine and
chlorine, which have to be considered as the cause of forest damage. Several
air pollutants may
mutually increase their effects. Unfavourable weather conditions and the
appearance of secondary
pests increase the damage.
Development of the Damage
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Forest damage has always existed: frost, drought and other natural stresses
have constantly attacked
our forests. In the vivinity of industrial plants, they were damaged by
polluted air. Moreover the
overcutting which humans practised in the forests for centuries has left
visible scars.
However, the present situation causes concern because now the damage of
forests, type, extent and
propagation of which are new, is even found in the supposedly "clean
air areas" which are far away
from any industry.
This damage was first observed in the middle of the 70s, initially to the
firs in the high elevations of
the north eastern Bavarian Middle Mountains. In the winter of 1980/81 spruces
and pines showed
striking needle loss in large areas of Bavaria. The first major damages
to the deciduos trees appeared
in the dry summer of 1982.
The damage to the forests is continuously monitored in long-term forest
observation areas, by the
investigation of bioindicators (mosses, lichens, conifers) and aerial survey
evaluation and forest
damage inventories.
The results of the forest damage inventory of 1988 show that:
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* 18% of the Bavarian Forests are seriously or averagely damaged (more
than 60% or 26 -
60% loss of needles or leaves).
* 39% are slightly damaged (1-25% loss of needles or leaves).
Recently the increasing number of damaged oaks is a primar issue for the
future research work.
4.1.2 Calamities in Forestry
Extreme weather conditions such as wet snow, storms, drought and frost
repeatedly cause serious
damage to German forests. Moreover animal or plant pests (e.g. bark beetles,
pine noctua/Panolis
flammea, nun moth/Lymantria monacha, gipsy moth/Porthetria dispar, oak
leafroller/Tortrix
viridana L. or fungi) can cause tree mortality and can even destroy complete
stands.
The greater the diversity of tree species, the more stable is the natural
balance of the forest as a living
comunity. This is another important reason for planting mixed stands instead
of the more susceptible
(spruce) monocultures. Site-adapted silviculture employing intensive tending
and particular measures
for biological forest protection can provide prophylactic action against
mass reproduction of forest
pests (tending of birds, bats and ants).
To prevent the reproduction of bark beetles, the breeding material suitable
for the pest must be
removed, e.g. by burning the bark. Bark beetle traps are used to monitor
and control the number of
beetles.
In Germany storms are the most important non-biotic danger for forests.
The recent storms of the
year 1990 (Vivian and Wiebke) showed the immense susceptibility of a great
part of German forests,
especially within instable conifer stands: A wood substance of about 75
mio m3 was the result of
these two storm events. This volume amounts to the 'normal' logging of
almost two years. The
consequences for the German timber trade were dramatical. An irresistible
slump of the pit-head
prices for spruce wood (average quality), e.g. in South-West Germany from
167 marks/m3 before the
storm event (January 1990) to 93 marks/m3 (regionally even less) afterwards
(April 1990), and the
immense volume of wind damaged wood had a harmful effect on the German
forest economy.
Another consequence was the problem of timber storage over a long period.
The state forest
authorities had to pay regard to the pivate forest owners concerning the
lumber merchandising on a
shaked timber market.
After clearing the storm damage large and woodless areas had to be reestablished.
Private owners
received financial subsidies from the government in order to compensate
their losses in selling the
wood for a low price.
4.1.3 Browsing of Game and Natural Regeneration
Our local game is dependent on the forest for its habitat. Too much game
can cause substantial
damage in the forests, however. In view of the threat, primarily to the
older forest stands, from the
new types of damage, natural locally adapted young forests must be able
to grow up as rapidly as
possible. The precondition is a stocking of game suitable for the local
conditions. The forests would
regenerate naturally over wide areas; but often the young trees - especially
deciduous trees and fir
(abies alba) - are browsed by roe deer, red deer and chamois and thus cannot
grow. Another effect is
that spruce and pine regenerate on these stands which causes a repressing
of decidous trees and fir
("Verfichtung") even on those sites which are not naturally suitable
for spruce and fir.
Moreover red deer cause substantial damage by debarking trees. The interaction
of forest decline and
game damage is especially critical where expensive fencing fails to give
protection, due to deep snow
and steep slopes in the mountain forests. In some regions of Germany broadleaved
species wouldn't
have any chance to regenerate naturally or grow up at all if the stands
were not protected by fences.
In planning the game harvest, the state of the vegetation, especially of
the regeneration, is used as an
index of the tenable game density. The forest authorities sample data on
browsing damage done to
young trees and prepare a status report on the state of regeneration. Forest
owners, hunting
cooperatives and the owners of the hunting right as well as the hunting
authorities receive this report
which is then used as a guideline for planning the annual game harvest.
4.2 Trends and Conflicts between Forestry, Nature Conservation and Recreation
In Germany there also exist plenty of problems concerning the appropriate
forest management. The
plurality of different interests as to the forest causes conflicts between
the different land users as well
as between people who are handling with forest for any other reason (e.g.
forest owners,
environmentalists, hunters, naturalists, people doing wintersports or other
recreational activities,
etc...).
In the last few years the controversy between forestry and nature conservation
more and more got
into public discussion. But forestry and nature conservation have much
in common, and there are
many modes of procedure inherent to the system which coincide with the
aims of nature
conservation. Saying, that forestry is applied nature conservation, however,
is too simple and
expressed in such short words even wrong. In many sectors of biotope and
endangered species
protection in the forest, much more can be done especially if mutual information
and confidence
increase.
Nature conservation and forestry have to be conscious about their responsibility
also for those parts
of nature which are neither directly used by man nor appear in lists for
endangered species. Especially
forestry's aims should not only be concentrated on anthropocentric concepts,
even though its dealings
- production of raw material that is environmentally friendly, utmost abstention
from the use of toxic
substances, and an operation that is altogether relatively natural - are
less problematic than those of
other land users.
From the viewpoint of nature conservation, a number of demands are formulated
in respect to forestry:
Forestry should not be restricted to timber production only; there had
to be a development towards
multi-functional forestry according to the laws of nature. In this sense,
high value yields could be
achieved; and yet close orientation towards natural tree species composition
would be possible, thus
satisfying both economical and ecological demands.
Forestry defined in such a way could offer structural multitude on a defined
area and thus also a
maximum of ecological and economical stability. The aspired structural
abundance would make
possible a profusion of small animal habitats and consequently also expanse
for adventure and a high
recreational value for people themselves.
For the public forests, nature conservationists and a more critical public
are expecting realization of
their demands. In private forests, many of these wishes - yet not all of
them - are fulfilled
automatically as many large private forestry enterprises managed in accordance
with the laws of
nature have proved in the past. For the remaining services, private forest
owners should be offered
programs that are similar to those for landscape preservation of the Bavarian
Ministry for the
Environment, or respective plans of the Bavarian Ministry of Agriculture
for farmers. Under such
conditions, demands of nature conservation towards forestry could be fulfilled
not only by the state
forests but also on private woodlands without economical losses by their
owners.
Another conflict potential cause the increasing leisure time activities.
Because of the growing mobility
more and more people are visiting forests to enjoy their outdoor activities
such as mountain biking,
skiing, horseback riding, canoeing, paragliding and others or just to enjoy
nature. In that way the
social function of forest gets more and more important. Conflicts between
forest administration and
people looking for recreation in or nearby forests are unavoidable because
of their different
understanding of forest, forest management and timber production. The state
forest administration
could solve this problem by improving public relation activities and by
informing the public more in
detail.