Full text: Resource and environmental monitoring

  
parameters and between the lakes. The analysis of 
such parameters (e.g. water depth, surrounding 
landuse) in relationship to the optical lake water 
properties shows also the influence on the trophic 
state. 
2. STUDY AREA 
The Northern Brandenburg lake district is located about 
80 km northwest of Berlin, Germany (see fig. 1). The 
surface morphology of the northern part of Germany 
was shaped by glaciers from Scandinavia. In this 
context the study area was mostly influenced by the 
Weichsel ice age during the Brandenburg phase 
(18000BP). The area is characterized by terminal 
moraines of the Frankfurter Staffel containing dead ice 
kettles and lakes of different stages of silting up 
(Gellert, (ed.), 1965). Soils of the area have been 
formed on substrates of varying loam and sand 
content. Beech stands, mixed forest, and coniferous 
stands (pine)  interfinger with cultivated areas 
(agricultural fields and pastures). Cultivated areas are 
dominated by large spatial units which are the result of 
cooperative farming in East Germany. Most of the 
settlements are small and the majority of people lives 
on agriculture, tourism, and services. 
       
       
working area 
Germany 
® 
München 
Fig. 1: Study area within the Northern Brandenburg 
lake district and location of ice marginal grounds 
‘Frankfurter Staffel’ determining its physiography 
The lakes of the study area (see fig. 2) differ in size, 
depth, catchment area, and trophic state. Many lakes 
are interconnected by natural streams or by man made 
canals. Some of the lakes are situated within small 
closed basins without surface tributaries (e.g., Lake 
Wummsee). The trophic state of the lakes ranges from 
oligotrophic to hypertrophic, while the majority of the 
lakes is classified as mesoptrophic lakes (MBLU 1996, 
Gewasserkataster, 1996 ). 
Chlorophyll-a concentration measured in the field for 
selected lakes (Thiemann et al., 1998) ranges from 1-3 
ug/l for lake GroBer Wummsee to 50-100 jug/l for lake 
Braminsee. Lake Wummsee has a maximum depth of 
36 m and its bottom is formed by sand and gravel. 
These characteristics and its isolated position as a 
closed basin lake led to a low nutrient content. The 
largest lake of the study area GroBer Stechlinsee has a 
maximum depth of 68 m and is the only one classified 
as  oligotrophic according to the determination of 
trophic state by Hôntzsch et al. (1993). Lake 
Braminsee represents the opposite side with its shallow 
depth of about 2 m and its high nutrient content being 
the result of an advanced stage of silting up. 
  
Fig. 2: IRS-1C subset of study area 
(lakes: 1 - Gr. Wummsee, 2 - Gr. Zechliner 
See, 3 - Braminsee, 4 - Gr. Stechlinsee, 5 - 
Plátlinsee) covers an area by 25 km * 20 km 
3. OBJECTIVES 
The goal of this study is to combine the investigation of 
the spatial and seasonal variability of optical lake water 
properties with an assessment of parameters 
influencing the trophic state of lakes. The optical lake 
water properties reflect the intensity of bioproduction of 
algae which significantly influences the trophic state of 
lakes. 
For this purpose, multitemporal satellite data are 
analyzed for describing lake behavior, spatial variability 
and seasonal changes during the observed period of 
time between August 1996 and September 1997. 
Additionally, information about factors influencing lake 
water properties are organized within a GIS for further 
systematic analysis. For this purpose influencing 
factors are subdivided into local lake factors and 
watershed factors, which are analyzed in their 
importance for the trophic state of lakes. 
4. LAKE WATER ANALYSIS USING SATELLITE 
REMOTE SENSING 
4.1 Satellite data 
Data of the Indian Remote Sensing Satellite IRS-1C 
are available for Europe since spring 1996 with a 
repetition cycle of 24 days. For a ‘multispectral scene 
(25 m pixel size) the swath width is 140 km and for a 
130 International Archives of Photogrammetry and Remote Sensing. Vol. XXXII, Part 7, Budapest, 1998 
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