Full text: Resource and environmental monitoring

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panchromatic scene (5.8 m pixel size) it amounts to 70 
km. For this study the VIS/NIR bands (see tab. 1) of the 
LISS 3 sensor were used for 6 multispectral datasets 
(see tab. 2) which were acquired under cloudfree 
conditions. Additionally, a complementary panchro- 
matic scene was acquired for June, 2, 1997. 
  
Band 1 (VIS) 2 (VIS) 3 (NIR) 
  
  
  
  
  
À in um 0.52-0.59 0.62-0.68 0.77-0.86 
  
  
Tab.1: Spectral bands of IRS-1C LISS 3 sensor 
During field campaigns secchi disk transparency was 
measured for a varying number of lakes while the 
lakes Gr. Wummsee, Gr. Zechliner See, and 
Braminsee (fig. 2) were measured all the time. 
Additionally, water samples were taken for 
determination of chlorophyll-a content. 
  
  
  
  
  
  
  
  
  
  
  
IRS-1C scene Field measurements 
August/18/1996 - 
February/2/1997 - 
May/04/1997 May/15/1997 
June/2/1997 (incl. PAN) June/10/1997 
- July/23/1997 
September/1/1997 September/2/1997 
September/25/1997 September/25/1997 
  
Tab.2: Acquisition dates of IRS-1C scenes and dates of 
according field measurements 
4.2 Preprocessing 
Multitemporal analysis of IRS-1C scenes for 
investigating spatial and seasonal variations of lake 
properties requires a geometric and atmospheric 
correction in order to carry out comparisons between 
scenes. 
Geometric correction of all datasets is based on a map 
to image registration of the panchromatic scene by 
determination of ground control points from 1:25000 
topographic maps. All multispectral datasets were 
rectified by an image to image registration with the 
panchromatic scene being the master image. A RMS 
error of less than 1 pixel shows the good spatial 
correspondence between the geocoded scenes. For 
resampling the nearest neighbor method was applied 
in order to maintain the original gray values for 
atmospheric correction. 
For atmospheric correction (see fig.3) of the 
multispectral datasets the ATCOR-2 model (Richter, 
1990) was used. The correction is based on reference 
spectra measured by the field spectrometer for the two 
September scenes. With these spectra the calibration 
coefficients (gain / offset) were estimated and 
considered as stable for all scenes. The atmospheric 
parameters (visibility, adjacency) were adjusted for 
each scene using targets with lowest variability of 
radiance. The result are reflectance values stretched 
by standard coefficients to 256 digital numbers (8bit) 
are obtained which allow a comparison between the six 
acquisition dates of the multispectral scenes. 
For the analysis of the lakes a water mask was applied 
to the dataset. The mask represents the result of a 
maximum likelihood classification of surface cover 
types. In a next step, spectrally representative polygons 
were determined within the lake areas by visual 
analysis. The identification of these core lake areas 
was performed in order to exclude mixed pixels in the 
area of shore lines which are caused by vegetation and 
the influence of the lake bottom in shallow areas. For 
the purpose of avoiding any kind of ground signal in the 
water spectra, the results of secchi disk transparency 
measurements were analyzed in combination with 
bathymetric information especially for the shallow lakes 
to make sure that lake depth significantly exceeds 
secchi disk transparency. 
  
79 —e— Gr. Wummsee 
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60 —e-— Gr. Zechl. See 
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= original 
S 30 --.--- Gr. Wummsee 
© 
S 20 FN atmos. corr. 
10 ---@--- Gr. Zechl. See 
0 atmos. corr. 
2 2 Qa - A- - - Braminsee 
atmos. corr. 
IRS-1C Band 
  
  
  
Fig. 3 Original and atmospheric corrected spectral 
values of representative lakes for the 
September, 1, 1997 scene 
4.3 Approach for satellite-based lake water analysis 
The three broad spectral bands of the IRS-1C sensor 
within the VIS/NIR part of the spectrum offer a rather 
limited range of possible band-related indices for 
characterizing water properties, such as chlorophyll-a 
content and secchi disk transparency. In this study 
band to band relations in form of combinations of single 
bands by various arithmetic expressions were 
investigated and are called indices in the following. The 
spectral properties of water for IRS-1C are 
characterized by the peak in the visible green band 
caused by scattering due to water constituents, by 
chlorophyll-a absorption in the visible red band and by 
absorption due to water in the near infrared (see fig.3). 
The overall magnitude of spectra is dominated by 
scattering of light by algae. For the broad IRS-bands 
the strong chlorophyll absorption in the visible red is 
superimposed by scattering effects for lakes with high 
chlorophyll-à content. Based on an analysis of the 
average reflectance values of the three bands for all 
core lake areas, the mean value of band 1 (VIS green) 
and band 2 (VIS red) and the difference between band 
1 and band 3 (NIR) were chosen for further analysis. In 
order to compare the results with single-point field 
measurements and on a lake by lake basis within and 
between scenes, standard statistical parameters were 
calculated for each core lake area from the results of 
the calculation of the indices. The values of the indices 
are named as digital numbers (DN). 
Intemational Archives of Photogrammetry and Remote Sensing. Vol. XXXII, Part 7, Budapest, 1998 131 
  
  
  
  
 
	        
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