Full text: Technical Commission VIII (B8)

   
   
      
  
  
   
  
   
  
  
  
  
   
   
  
  
  
  
  
    
   
  
    
   
   
    
  
    
   
   
    
   
   
    
   
   
   
  
   
   
   
   
   
   
  
   
  
     
   
XXXIX-B8, 2012 
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stand volume in 
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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 
  
  
  
  
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Standard deviation of Sm DSM pixels 
Figure 3. Scatter plot and fitted curve 
After constructing the equation, those samples which have been 
holding out (20 percent) were used for calculating bias and root 
mean square error. Relative bias and RMSE were -5.8 and 49.8 
percent, respectively (table 2). 
Table 2. Bias, relative bias, RMSE and relative RMSE of stand 
volume estimation 
  
  
  
  
Bias (m^) -21.3 
Relative Bias (%) -5.8 
RMSE (m?) 183 
Relative RMSE (%) 49.8 
  
4. DISCUSSION 
In the present research, a new approach for estimating forest 
stand volume at plot level were presented and examined. It has 
been found that the most proper pixel size for modelling stand 
volume was 5 to 7 meter. Maybe, this is a consequence of this 
fact that the average size of tree crowns at study area was 
approximately 7 m. The smaller sizes contain some variation of 
crown surface and larger sizes cause a smoothing in height 
variation. 
Many researches have been conducted for estimating stand 
volume by remotely sensed data. When looking at accuracy 
expressed as a relative RMSE of stand volume estimation, using 
sattelite images, 45% (Mäkelä and Pekkarinen, 2004), 48% and 
19% (Mäkelä and Pekkarinen, 2001), 51% (Labrecque et al., 
2006), 64% to 295% (Katila and Tomppo, 2001), 56% (Hyyppä 
et al., 2000), 36% (Holmgren et al., 2000), 83% (Franco-Lopez 
et al, 2001), 41% (Wallerman et al., 2002), 36% (Hall et al., 
2006) and using aerial photographs, 57.8% (Tuominen and 
Pekkarinen, 2005), the present result is satisfactory. 
Tuominen and Pekkarinen (2004) achieved 66.1% RMSE, 
using modified colour-infrared aerial photographs and Sohrabi 
(2008) using colour infrared aerial images of UltraCamD 
reported 66.1 — 76.9 % RMSE at plot level. Here, we achieved 
49.8% RMSE which is a good improvement in precision of 
volume estimation of forest stands. 
One big problem in this method occurs when trees canopy cover 
Is totally closed. In this situation, the standard deviation of 
height is low while stand volume is high. In future studies, 
applying forest stratification could be studied. 
5. REFERENCES 
Altmaier, A., Kany, Ch. 2002. Digital surface model generation 
from CORONA satellite images. ISPRS Journal of 
Photogrammetry & Remote Sensing, 56: pp.221— 235. 
Franco-Lopez, H., Ek, A.R., Bauer, M.E., 2001. Estimation and 
mapping of forest stand density, volume, and cover type using 
the  k-nearest neighbors method, Remote Sensing of 
Environment, 77: pp.251-274. 
Gruber, M., Schneider, S., 2007. Digital surface models from 
UltraCam-X images, Photogrammetric Image Analysis, 
Munich, Germany, 36 (3/W49B), pp.47-52. 
Hall, R.J., Skakun, R.S., Arsenault, E.J., Case, B.S., 2006. 
Modeling forest stand structure attributes using Landsat ETM+ 
data: application to mapping of aboveground biomass and stand 
volume, Forest Ecology and Management, 225: pp.378-390 
Holmgren, J., Joyce, S., Nilsson, M., Olsson, H., 2000. 
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by combining satellite image data with field data, Scandinavian 
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Hyyppä, J., Hyyppà, H., Inkinen, M., Engdahl, M., Linko, S., 
Zhy, Y.H., 2000. Accuracy comparison of various remote 
sensing data sources in the retrieval of forest stand attributes, 
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Katila, M., Tomppo, E., 2001. Selecting estimation parameters 
for the Finnish multisource National Forest Inventory, Remote 
Sensing of Environment, 76: PP.16-32. 
Kellndorfer, J.M., Dobson, M.C., Vona, J.D., Clutter, M., 2003. 
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Mákelà, H., Pekkarinen, A., 2001. Estimation of timber volume 
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Mäkelä, H., Pekkarinen, A., 2004. Estimation of forest stand 
volumes by Landsat TM imagery and stand-level field- 
inventory data, Forest Ecology and Management, 196: pp.245— 
255, 
Maltamo, M., Packalen, P., Yu, X., Eerikainen, K., Hyyppa, J., 
Pitkanen, J., 2005. Identifying and quantifying structural 
characteristics of heterogeneous boreal forests using laser 
scanner data, Forest Ecology and Management, 216: pp. 41-50. 
Patenaude. G., Milne, R., Dawson, T.P., 2005. Synthesis of 
remote sensing approaches for forest carbon estimation; 
reporting to the Kyoto Protocol. Environmental Science and 
Policy, 8, pp.161-178. 
Sohrabi, H., 2009. Application of Visual and Numerical 
Interpretation of Aerial Images in Forest Inventory, PhD thesis 
in Tarbiat Modares University, 114 pp. 
Tuominen, S., Pekkarinen, A., 2004. Local radiometric 
correction of digital aerial photographs for multi source forest 
inventory, Remote Sensing of Environment, 89: 72-82. 
Tuominen, S., Pekkarinen, A., 2005. Performance of different 
spectral and textural aerial photograph features in multi-source 
forest inventory, Remote Sensing of Environment, 94: pp.256— 
268. 
Wallerman, J., Joyce, S., Vencatasawmy, C.P., Olsson, H., 
2002. Prediction of forest stem volume using kriging adapted to 
detected edges, Canadian Journal of Forest Research, 32: 
pp.509—518.
	        
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