Full text: Proceedings; XXI International Congress for Photogrammetry and Remote Sensing (Part B1-1)

The International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences. Vol. XXXVII. Part Bl. Beijing 2008 
383 
Figure 4. canopy height of OK and OCK models 
From figure4 and figure5, we can find that the result of OK is 
similar to that of OCK model. But comparing the predicted 
canopy height with the field measurement of the canopy height, 
the precision of OCK model is prior to that of the OK. However, 
the R 2 coefficient of needle forest is less than that of the 
broadleaf forest. Cokriging proved slightly more accurate than 
kriging. The spatial models, kriging and cokriging, produced 
greater biased results than regression and poorly reproduced 
vegetation pattern. This mar be related with the distribution of 
lidar sampling points. 
Needle Forest + Kriging 
Field Measured Height 
Broadleaf Forest + Kriging 
Field Measured Height 
Field Measured Height 
Broadleaf Forest + CoKriging 
Field Measured Height 
Figure 5. Compare of the results of OK and OCK models 
4.4 Results of integration model 
Due to the precision of OCK is greater than that of OK. Here, 
we have only discussed the integration model of 
‘OCK+regression’. Residuals from the OLS regression were 
imported into cokriging. The result was illustrated in the 
figure6(b). 
(a) Regression (b) CoKriging+Regression 
Figure 6. canopy height of integration model 
Through comparing the field measurement of canopy height 
with the predicted canopy height, the R 2 coefficient of needle 
forest is 64.44%, which greater than that of the broadleaf 
forest(60.95%). Obviously, this results are greater than that of 
OK/OCK. The the R 2 coefficient of broadleaf forest is also 
greater than that of the OLS (50.62%). However, the R~ 
coefficient of needle forest is less than that of the OLS(69.2%). 
This is related with the distribution of lidar sampling points. An 
equitable distribution of lidar sampling points proved critical 
for efficient lidar Landsat TM/ETM+ integration (Hudak et al. 
2002). 
0 2 4 6 8 10 12 14 16 18 20 22 24 0 2 4 6 8 10 12 14 16 18 20 22 24 
Field Measured Height Field Measured Height 
Figure 7. Measured canopy height Vs. predicted canopy height 
4.5 Discussion 
The results from this study confirm that forest height can be 
estimated using GLAS waveform combination with the terrain 
index in sloped area. Regression equations explained 51.0% and 
84.0% of variance for broadleaf and needle forest respectively, 
the result of this work indicate that the terrain index will help to 
extract the forest canopy height over a range of slopes. 
Integration of GLAS and Landsat TM/ETM+ data using 
empirical modeling procedures can be used to improve the 
utility of both datasets for forestry applications. In this study, 
four integration techniques: OLS,OK,OCK and OCK+OLS 
models, were compared. In total, the integrated technique of 
ordinary cokriging of the height residuals from an OLS 
regression model proved the best method for estimating the 
forest canopy height. In future work, to improve the accuracy of 
the cnaopy height estimations and test the integration models in 
the sloped area once lidar sample data become readily available. 
REFERENCES 
Craig Markwarddt, http://cow.physics.wisc.edu/~craigm/idl/ 
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Cohen, W.B., Spies, T.A., 1992. Estimating structure attributes 
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Finney, M.A., 1998. FARSITE: Fire area simulator -model 
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Hudak, A.T., Lefsky, M.A., Cohen, W.B., Berterretche, M., 
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Hyde, P., Dubayah, R., Walker, W., Blair, J.B., Hofiton, M., 
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