Full text: Resource and environmental monitoring (A)

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IAPRS & SIS, Vol.34, Part 7, "Resource and Environmental Monitoring", Hyderabad, India, 2002 
  
to the large disk space requirement (about 2 GB) and data 
handling, the 32 bit real 0° images were converted to 8 bit 
unsigned images. A user defined linear relation was used for 
this purpose, so that once 8 bit DN values were extracted from 
image, later on it can be inverted to get backscattering 
coefficient values in order to carry out quantitative analysis. 
5.6 Image registration 
Adjacent path SAT images of IRS L-III were mosaiced 
sidewise. The RADARSAT EL1 image was geo-referenced and 
IRS LISS-III image was co-registered with respect to ELI 
image keeping RADARSA-1 ELI image as reference image 
nearest neighborhood method of resampling (Duggin and 
Robinore, 1990). 
5.7 Signature extraction 
After registering both the images sampling locations were 
identified on the images. Backscatter coefficient values for 
sampling locations were extracted from SAR image. IRS L-III 
data was used to classify crop covered soil and bare soil in 
order to avoid the inclusion of crop covered fields in the 
analysis. 
5.8 Model development 
Variation in SAR signature due to soil moisture was studied for 
agricultural areas at lower incidence angle (16°) using the 
backscatter values extracted from RADARSAT-1 Extended 
Low-1 beam mode SAR image. Soil moisture retrieval models 
had been done for the following combinations using linear 
regression analysis. 
-  Backscattering coefficient with gravimetric soil 
moisture. 
-  Backscattering coefficient with volumetric soil 
moisture. 
- . Backscattering coefficient with soil moisture 
represented in terms of percentage of field capacity. 
- . Backscattering coefficient with soil moisture 
represented in terms of percentage of available water. 
After the development of soil moisture retrieval models with 
the different values of soil moisture a comparative evaluation of 
different models has been performed. 
6. RESULTS AND DISCUSSION 
In order to express the soil moisture in a more realistic way so 
that it should be less sensitive to soil texture and more useful 
for agricultural applications, four separate models have been 
developed using the soil moisture values in terms of 
gravimetric soil moisture, volumetric soil moisture, soil 
moisture in percentage of field capacity and soil moisture in 
percentage of available water. Since objective of the present 
study was to incorporate the effect of soil texture in the soil 
moisture retrieval model, enough care has been taken to avoid 
the effects of other noise parameters like crop cover and surface 
roughness. Absence of other noise parameters would enhance 
the effect of soil texture on the radar backscatter. For this 
purpose only bare fields have been included in the analysis in 
order to avoid the 2-way attenuation in radar backscatter 
coefficient. Moreover out of all the bare fields only those fields 
have been included in the analysis, which were smooth or 
having small values of surface roughness. Results of all these 
models are given in Table 2. Table 2 indicated that there is a 
723 
significant increase in R? for model developed with the values 
of soil moisture in terms of percentage of available water. R? 
increased from 0.86 to 0.93 by represent ting the soil moisture 
in percentage of available water instead of gravimetric soil 
moisture. A marginal increase in R? was also observed from 
0.86 to 0.88 in case of replacing gravimetric soil moisture with 
volumetric soil moisture. R? has further increased from 0.88 to 
0.90, when volumetric soil moisture has been replaced by soil 
moisture in percentage of field capacity. Similar results have 
been observed by Ulaby et. al., (1986b) by expressing the soil 
moisture in terms of percentage of field capacity. Study 
indicated that gravimetric soil moisture and volumetric soil 
moisture are less sensitive way to represent soil moisture while 
using microwave remote sensing technique. This is due to the 
fact that gravimetric soil moisture and volumetric soil moisture 
does not take into account the relative proportions of various- 
sized particles in a given soil medium which is one of the main 
factors governing the relative percentage of bound water and 
free water in the mixture of soil and water (wet soil). Since 
field capacity and wilting point of a particular soil are directly 
linked with the soil texture and microwave are sensitive to 
proportion of free water and bound water in a given soil hence 
the last two models were found to be better than the first two 
models. In particular the forth model developed with the values 
of soil moisture in percentage of available water was found to 
be the best with the highest value of R?. 
  
  
  
MODEL USED Coefficients 
Soil Moisture = A + B * 0° | A B R° 
Soil Moisture (weight) 46.2 3.6 0.86 
=A+B*o° 
where Soil-Moisture(weight) 
represents gravimetric soil 
moisture 
Soil Moisture (volume) 67.9 5.4 0.88 
=A+B*o° 
where Soil-Moisture(volume) 
represents volumetric soil 
moisture 
Soil Moisture (% r.c., 168.6 13.4 | 0.90 
=A+B*o° 
where  Soil-Moisture(ær.c.) 
represents soil moisture in 
percentage field capacity 
Soil Moisture (% A.w.) 224.8 19.7 | 0.93 
=A+B*o° 
where Soil Moisture, ow.) 
represents soil moisture in 
percentage of available 
water. 
  
  
  
  
  
  
  
  
  
Table 2. Results of various models developed with different 
units of soil moisture 
7. CONCLUSIONS 
Study indicated that percentage of available water is a more 
realistic way to represent soil moisture as it directly describes 
the parameter affecting microwave interaction in the soil 
medium. Thus it is possible to reduce the effect of soil texture 
in the sensitivity of microwaves towards the soil moisture. The 
concept of available water in a soil medium is based upon the 
assumption that the water present in the soil medium at 15-bar 
pressure, which is unavailable to plants, is actually the bound 
 
	        
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