Full text: Technical Commission VII (B7)

  
International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences, Volume XXXIX-B7, 2012 
XXII ISPRS Congress, 25 August — 01 September 2012, Melbourne, Australia 
  
  
prises unt 
Unchanged 
c: Hash Baishfness 
High Greenness 
  
High Wetstess 
Media Briditness 
Medii: Or eeunesá 
  
S Medium Wetaess 
  
  
  
Figure 6. ISODATA classification image 
In Figure 6 each class indicates intensity of vector change in 
any direction within the Tasseled Cap Transformation. 
  
  
  
  
  
  
Class Value Area (ha) % 
0 No change 24716.44 86.51 
1 High wetness 350.12 1.22 
2 High greenness 650.88 2.28 
3 High brightness 1282.20 4.49 
4 Medium wetness 131.20 0.46 
5 Medium greenness 1296.60 4.54 
6 Medium brightness 142.56 0.50 
  
  
Table 3. Landscape dynamic classes and their corresponding 
area in the Terkos 
After image classification, accuracy of the resultant image was 
assessed. Accuracy assessment is very important for 
understanding the detected change results and employing these 
results for land management, urban land planning and decision- 
making (Foody, 2002). In this study, overall accuracy and 
Kappa analysis were used to perform classification accuracy 
assessment based on error matrix. Overall accuracy and Kappa 
statistics were calculated as 84.32 % and 0.81, respectively. 
5. CONCLUSIONS 
In this study, mCVA used to detect the most dynamic areas in 
Terkos Water Basin, Istanbul. Three TC features (brightness, 
greenness and wetness) were derived for SPOT 5 MS data to 
produce three difference, one magnitude and three direction 
images using 2003 dated SPOT 4 and 2007 dated SPOT 5 MS 
data. Classified vector magnitude and direction components 
were used for the selection of dynamic landscapes. The 
advantage of the mCVA is it has the ability to process any 
number of spectral bands but it is difficult to decide changed 
classes and threshold value. The sensitivity of the CVA was 
enhanced by using polar coordinates to represent vector 
directions. CVA and extended polar coordinates improved the 
ability to determine landscape dynamics in this heterogeneous 
environment. 
ACKNOWLEDGMENT 
The authors would like to thank the SPOT OASIS project for 
providing the 2007 dated SPOT 5 MS and PAN images. 
REFERENCES 
Balik Sanli F., Bektas Balçik F., and Goksel C., 2007. Defining 
temporal spatial patterns of mega city Istanbul to see the 
   
impacts of increasing population. Environmental Monitoring 
and Assessment, 146, 1-3, pp. 267-275. 
Bektas Balçik, F., 2010. Mapping and Monitoring Wetland 
Environment by Analysis of Different Satellite Images and Field 
Spectroscopy’. Istanbul Technical University, PhD thesis. 
Chavez, P. S., 1988. An improved dark-object subtraction 
technique for atmospheric scattering correction of multispectral 
data. Remote Sensing of Environment, 24, pp. 459—479. 
Chen, J., Gong, P., He, C. and Shi, P., 2003. Land-use/land- 
cover change detection using improved change-vector analysis. 
Photogrammetric Engineering and Remote Sensing, 69, pp. 
379. 
Coppin, P., Jonckheere, I., Nackaerts, K., Muys, B., Lambin, E., 
2004. Digital change detection methods in ecosystem 
monitoring; a review. International Journal of Remote Sensing, 
25, pp. 1565-1596. 
Coskun, H. G., Gulergun, O., Yilmaz, L., 2006. Monitoring of 
protected bands of Terkos drinking water reservoir of 
metropolitan ‘Istanbul near the Black Sea coast using satellite 
data. International Journal of Applied Earth Observation and 
Geoinformation, 8, pp. 49-60. 
Crist, E.P., and Kauth, R. J., 1986. The Tasseled Cap de- 
mystified. Photogrammetric Engineering and Remote Sensing, 
52, pp. 81-86. 
Flores, S. E., Yool, S. R., 2007. Sensitivity of change vector 
analysis to land cover change in an arid ecosystem. 
International Journal of Remote Sensing, 28, pp. 1069-1088. 
Foody, G. M., 2002: Status of land cover classification accuracy 
assessment. Remote Sensing of Environment. Vol. 80, pp. 185- 
201. 
Green, K., Kempka, D. and Lackey, L., 1994. Using remote 
sensing to detect and monitor land-cover and land-use change. 
Photogrammetric Engineering and Remote Sensing, 60, pp. 
331-337. 
Ivits, E., Lamb A., Langar, F., Hemphill, S., Koch, B., 2008. 
Orthogonal transformation of segmented SPOT 5 images: 
Seasonal and geographical dependence of the tasseled cap 
parameters. Photogrammetric Engineering & Remote Sensing, 
74, 11, pp. 1351-1364 
Lambin, E.F., and Strahler, A. H., 1994. Change vector analysis 
in multi- temporal space: A tool to detect and categorize land- 
cover change processes using high temporal-resolution satellite 
data. Remote Sensing of Environment, 48:231—244. 
Lillesand, T. M., and Kiefer, R. W., 1987. Remote Sensing and 
Image Interpretation (New York: John Wiley & Sons). 
Lu, D., Mausel, P., Brondizio, E., and Moran, E., 2004. Change 
detection techniques. International Journal of Remote Sensing, 
25, pp. 2365—2407. 
Malila, W.A., 1980. Change vector analysis: an approach for 
detecting forest changes with Landsat. Proceedings of the Sixth 
Annual Symposium Machine Processing of Remotely Sensed 
Data, Purdue University, West Lafayette, IN, pp. 326-335. 
   
 
	        
Waiting...

Note to user

Dear user,

In response to current developments in the web technology used by the Goobi viewer, the software no longer supports your browser.

Please use one of the following browsers to display this page correctly.

Thank you.