All countries of western Europe use these
damage classes according to the table
(1) in their forest damage inventory.
The test site located at St. Blasien in
the (Black Forest) FRG consists the
following tree speceis: spruce = 84%, fir
= 3% Beech and Maple = 8% and others =5%
with a mix of different age classes. Most
of the test site is located at an alti
tude between 800 and 1400m above mean sea
level. The PH value in the forest soil at
this site as determined 25 years ago was
4.4 and now is dropped to 2.2-3.0 . The
annual precipitation at this altitude is
approximately 1500 mm and mean annual
temperature is 5,5-5,9 Celsius . (This
information comes from the forest service
at St.Blasien/ Schluchsee in the Black
Forest).
The forest decline situation at the Erz
gebirge site differs from the test site
at St. Blasien in the areal extent and
damage degree. The Erzgebirge region is
more than 110 km long and 20-25 km broad
and contains a very large forest area
characterised by very high forest damage,
totaly dead forest area and clear cut
forest area. This large area means, in
the case of an observer on the ground the
distance between one horizon to the
other. The air pollution in the Erzge
birge region is very high. Czeckoslovakia
(CSFR), Poland and East Germany produce
large amounts of SO 2 mainly through heavy
industry and lignite power plants. There
are many lignite power plants in East
Germany and in Czeckoslovakia in opera
tion since the Second World War and some
of them existed even earlier. East
Germany is the world’s largest lignite
consumer, using over 300 million metric
tons per year. Most of the lignite is
used by thermal power stations supplying
over 83 % of the country' electricity
needs. The high sulphur content of this
fuel is the reason why the GDP has the
highest emissions of sulphur dioxide per
inhabitant in Europe. Poland and CSFR
also use lignite and produce nearly as
GDR (Acid Magazine No.8 September 1989).
There is no detailed information about
the tree species and their distribution
in the Erzgebirge region, due to the very
large area and lack of published data
from such GDR and CSSR. The Forest Ser
vice in CSFR has provided roughly in
formation, suggesting that the study site
consists of the following species: Norway
spruce, white fir, European larch, pine,
and douglas fir totallings (83%) of the
forested areas. The dominant species is
spruce but in addition Beech/Oak (7%) and
other species (5%). The test site is lo
cated at altitude between 360 m and 1244
m above mean sea level. Other information
such as the annual volume of preci
pitation, temperature and pH value in the
soil, are not available at present.
Due to the unavailable information from
this test site (Erzgebirge) such as in
frared color aerial photography or detail
ground information, the author construc
ted special classes according to his ex-
perince in the Black Forest regarding the
forest situation and the size of the
study area.
The determined classes are:
a- healthy and slightly damaged conife
rous stands
b- damage and severely damaged coniferous
stands
c- dying and dead coniferous stands
d- clear cut area
e- deciduous stands
The current research focus is to develop
and establish a methodology based on the
evaluation of Landsat imagery as one mean
of forest damage assessment and not to
replace conventional inventory methods
such as ground checking and the inter
pretation of infrared aerial photographs.
Use of these two conventional methods for
forest damage assessment of forest
decline for large areas such as the Erz
gebirge is not a practicable method at
present for rapid forest damage inven
tory. The current research makes use of
the Landsat imagery processed via a com
puter-aided evaluation for forest damage
assessment, mapping, and change de
tection .
2 Material and Methods.
The test site located at St. Blasien in
the Black Forest, is supported by much
essential informations, because the test
site has been used for many years as a
test site for a project dealing with use
of airborne multispectral scanner data
(TM-Simulation=TMS) taken from different
altitudes for the investigation of the
spectral reflectance properties and their
use for the classification of forest da
mages conditions.
In addition to the Airborne multispectral
data, aerial IR-Color photography, at the
scale 1:5000, has been taken in support
of the multispectral data acquisitions.
Another kind of information is the ground
truth of different stands in the test
site .
The results that were acquired through
the interpretation of aerial CIR-photo-
graphs and analysis of the acquired
ground truth data have been used for
selecting of training areas representing
different levels of damages or the veri
fication of the results that were achived
by the computer-aided classification
approach to analyzing TM/TMS data.
Two Landsat-TM scenes were ordered for
investigation and evaluation. The dates
of the scenes are September 12. 1985 and
June 27, 1986 with coordinate 195/27.
Both scenes have good data quality and
are without cloud cover.
The Erzgebirge site has no additional in
formation such as ground truth data or TR
color aerial photographs. The only
available data for this site are the
Landsat in,ages from 1972-1987.
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