Full text: XVIIth ISPRS Congress (Part B5)

   
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Laboratory Field 
  
Treatment f m T sitel  site2 
tsa/ma 
relation between | before and |1.12 1.27 1.44 | 1stdate 1.34 1.22 
total surface area | afterrain |1.02 1.14 1.37 | 2nddate 1.23 1.13 
and map area 
RRC 
Index according | before and [2.3 43 85 Istdate 7.7 53 
to Currence and after rain 11:4 3.2 7.5 2nd date 7.0 4.0 
Lovely (1970) 
  
  
  
  
  
  
Table 2: Indices from microrelief describing DEMs 
the field. An increase in the microrelief roughness 
doubled the value for RRC. The microrelief differences 
are well characterized by this index. For the field ex- 
periments the decrease of RRC due to rainfall was minor 
than but still comparable to that of the laboratory 
treatments. Thus both indices seem to be capable to 
characterize microrelief and changes due to rainfall in 
the field as well as in the laboratory. 
Semivariograms were calculated in order to identify 
possible spatial patterns. Figs. 3a and 3b show semi- 
variograms for the rough and fine surfaces, each before 
and after rainfall. In the beginning all curves show a 
sharp rise with the lag, until a sill is reached at greater 
lag values. The range within which a spatial dependence 
of the investigated parameter is visible, is marked by 
arrows in the figures. For the rough surface, the range 
corresponds to a lag h of 25, while the range is about 
12 to 14 in the medium treatment, not shown here. 
These lag values are equivalent to 50 mm and 25 mm, 
respectively (1 h = 2 mm). This corresponds to the open- 
ings of the sieves that were used to fill in the soil 
material and depicts the maximum diameters of the 
largest aggregates or clods in each microrelief type. 
After rainfall range tended to increase slightly, which 
might be due to a relative flattening of the bigger 
clods. Thus, with the help of semivariograms, it is 
possible to confirm the importance of big clods as 
surface shaping elements. For the fine treatment there 
is no clearly identifiable sill, just a lowered gradient in 
the range of 7 to 10. In this case there is no reliable 
identification of the largest clods (10 mm diameter) 
since this is just four times the height value spacing 
and within this comparably high-frequent range no 
characteristic sill is possible. The sills in the semivario- 
grams are significantly different. Rainfall led to a relative 
reduction of the sill by about 2096 for the rough, 5096 
for the medium, and 2596 for the fine treatment, respect- 
ively. The absence of nugget variance in all semivario- 
grams indicates that the grid distance is small enough 
to fully characterize the variation in surface microrelief. 
Higher resolution in microrelief variation would not 
yield any further information. Results of the semivario- 
grams from the field experiment DEMs were similar to 
those of the medium treatment above. Here nugget 
variance was missing, too. 
Semivariance 
  
  
  
  
  
  
  
  
  
  
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a) Lagh 
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Semivariance 
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b) Lagh 
Fig. 3: Semivariograms for (a) rough and (b) fine surfaces 
before and after rainfall (lag h = 2 mm). 
Energy dissipation 
The kinetic energy of raindrops impinging on the soil 
surface leads to surface sealing, which is the actual 
trigger mechanism for runoff formation. As discussed 
earlier, the TSA/MA ratio affects the total input of rainfall 
energy. The effective normal component of impact force 
with respect to impact angle is also relevant to splash 
detachment and thus to sealing. Table 3 shows the 
calculated effective energy (the normal component of 
impact force with respect to the TSA) in percent of the 
kinetic energy as simulated in the laboratory experi- 
ments. 
  
  
Laboratory Field 
Treatment f m r site 1 site 2 
E.eff (%) 
before and 84 65 56 1st date 62 71 
after rain 95 80 67 2nd date 71 82 
  
  
  
  
Table 3: effective rainfall energy E.eff (/m* tsa) in per- 
cent of the kinetic rainfall energy (J/m* ma) 
The effective rainfall energy for the rough treatments 
is only about one half of its kinetic energy. This share 
is significantly larger for the medium and fine areas. 
Even after the rain there is considerable energy reduct- 
ion in the rough and medium areas. To verify the 
theory that the microrelief induced effective rain energy 
substantially influences silting and surface runoff, we 
must compare the runoff measured in the laboratory 
with the effective rain energy. Figures 4a and 4b show 
runoff curves. In fig. 4a the cumulated runoff is plotted 
against cumulated kinetic energy as it is usual in 
literature. 
   
   
   
    
   
   
  
   
  
  
    
  
   
  
  
  
  
    
  
  
  
  
  
  
   
  
  
  
   
   
   
  
  
   
   
   
   
   
  
  
  
  
   
  
  
  
   
  
  
  
   
  
   
   
   
  
  
  
    
	        
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