Full text: Technical Commission VIII (B8)

    
    
  
    
B8, 2012 
0.12. Note that 
1 cover of 0.0). 
  
  
  
  
| ue 
5 | 070 | 
1 07% | 
3 | 059 | 
2 0.74 
  
  
  
green cover on 
d Biomass 
nding measured 
across sites and 
rin. kg ha) 
1s for dates up 
974) plotted by 
e the maximum 
easured biomass 
'ression model: 
(l) 
. The regression 
y NDVI did not 
s as it did for 
lues. Pooling all 
ue of 0.13 and 
nsors (ACS 470 
ta was subset to 
0 Horsham data 
comparison was 
d the highest 
[. One possible 
ity of the sensor 
ie to the small 
en sensor NDVI 
biomass. Linear 
ysham data for 
nclusive), which 
: of 115 kg ha” 
  
  
International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences, Volume XXXIX-B8, 2012 
XXII ISPRS Congress, 25 August — 01 September 2012, Melbourne, Australia 
  
pe 
  
12000 7 
10000 4 = o ACS 470 
8000 — 
6000 - 
4000 + 
2000 + 
Biomass, as Dry Matter kg ha-1 
  
D 
e ACS 210 
0.4 
Sensor NDVI 
  
  
  
  
Figure 2. Above ground biomass measured as dry matter kg 
ha! plotted against the mean NDVI measured by 
plot for all data up to the flowering stage, Zadoks 60 
(N=1475). The non linear equation fitted yield re 
0.27 and a standard error of 2133 kg ha”. 
  
Std. Error (kg ha’! 
  
  
  
  
  
  
  
  
  
  
  
  
  
  
Sensor N r 
All Dates 
All Sensors 1858 0.13 3459 
ACS 470 1214 0.03 3599 
Greenseeker 379 0.30 3017 
ACS 210 
Until Flowering (Zadoks 60) 
All Sensors 1477 0.27 2133 
ACS 470 947 0.22 2377 
Greenseeker 195 0.37 1537 
ACS 210 265 0.64 372 
ACS 210 148 0.67 115 
Low 
biomass* 
  
  
  
* Fitted linear regression to data with 0 < DM < 1000 kg ha 
Table 3. Regression results for Total Above Ground Dry 
Matter (kg ha") on NDVI 
4. CONCLUSIONS 
The commercially available active optical sensors are robust 
and can be used under most sky conditions, so they are of 
potential interest for ground truth of biomass for various remote 
sensing applications. The results show a strong linear relation 
between the sensor NDVI and fractional green cover for a 
dataset that included three different sensors and multiple sites 
and dates. However, the relation between measured biomass and 
sensor NDVI was found to be linear only at low values of 
biomass (less than 1000 kg ha), and non-linear regression 
resulted in low r? values for the dataset. Results of the study 
indicate the sensors may provide good estimates of fractional 
green cover, although caution should be applied when directly 
comparing NDVI from different sensors models. 
5. REFERENCES 
Li, Y., Chen, D., Walker, C.N., Angus, J.F., 2010. Estimating 
the nitrogen status of crops using a digital camera. Field Crops 
Research 118(3), pp. 221-227. 
Payne, R.W., Murray, D.A., Harding, S.A., Baird, D.B., Soutar, 
D.M., 2009. GenStat for Windows (12th Edition) Introduction. 
VSN International, Hemel Hempstead. 
Rouse, J.W., Jr., Haas, R. H., Schell, J.A., Deering, D.W, 1973. 
Monitoring vegetation systems in the Great Plains with ETRS. , 
Earth Res. Tech. Satellite-1 Symp, Goddard Space Flight Cent., 
Washington, DC, pp. 309-317. 
Zadoks, J.C., Chang, T.T., Konzak, C.F., 1974. A decimal code 
for the growth stages of cereals. Weed Research 14(6), pp. 415- 
421. 
6. ACKNOWLEDGEMENTS 
The authors wish to thank the Grains Research Development 
Corporation for research funding of multiple projects that 
supported the data acquisition and analysis of this work. We are 
also indebted to our grower collaborators who allowed us to 
work on their farms. 
    
   
    
  
   
  
    
   
  
  
   
    
  
   
    
   
    
   
    
  
   
  
   
   
  
    
   
   
   
  
    
  
  
  
   
   
     
  
	        
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