seto, k.c., woodcock, c.e., song, c. huang, x., lu, j. and kaufmann, r.k. (2002). monitoring...
TRANSCRIPT
Seto, K.C., Woodcock, C.E., Song, C. Huang, X., Lu, J. and Kaufmann, R.K. (2002).
Monitoring Land-Use change in the Pearl River Delta
using Landsat TM.
International Journal of Remote Sensing, 23(10): 1985-2004
David Black10/02/2006
OUTLINE
• Economy of the area
• Why monitor land use change
• Land-use and Land cover
• Change detection techniques available
• Study area and pre-processing
• Methodology
• Accuracy assessment
• Main findings
• Conclusions
Why the need to monitor land-use change in he area
• Better understand socio-economic driving forces behind land-use change
• As socio economic activity rises, land available for agricultural practices is limited
Constraints surrounding the Pearl River Delta
• Increased demand for: • Transportation networks
• Residential, industrial and commercial construction
Economy of the area
• Fastest developing regions
• 1985 – 1997 15.3% increase in GDP
• Establishment of Special Economic Zones (SEZ’s)
• Foreign investment
Land-use and Land cover
• Land-use: corresponds to land-cover type i.e. how the land is used
• Land-cover: Measures physical attributes, conditions and characteristics of earth surface
Remote sensing and social sciences
• Recent use of satellite remote sensing in social sciences
• Integrate remote sensing with socio economic data
• Satellites observe land-cover not land-use
• Core requirement is that of how land is used
Change detection techniques available
• Image differencing, image regression, image ratioing etc
• No consensus to a “best” change detection technique
• Technique used depends on availability of data, study area, time and computing constraints and type of application
• Numerous studies carried out with difficulty in differentiating specific features
Advantages and disadvantages of Landsat Thematic Mapper
• Spatial resolution provides better discrimination of urban features
• Limited success from previous urban studies
• Spatial variance for urban environment is high
• Difficult to classify due to heterogeneous nature
STUDY AREA
(Source: Terraserver, 2006)
Shenzhen
• Co Registration
• Nearest neighbour resampling
• First order polynomial
• Landsat TM
• 10/12/1988 – 03/03/1996
• Root means squared (RMSE = 0.30 pixels)
• Radiometric correction
Pre - Processing
Methodology
• Accuracy of change map will at best be product of individual classification accuracy of each date
• These sources of error overcome using multi-temporal principal component technique
• Multidate Tasseled Cap transformation is scene dependent and proved successful in monitoring change
• Above method rotates TM data creating three planes (Brightness, Greenness and Wetness)
• Classification process involves five steps:
1. Define map classes
2. Associate land-covers with land-uses
3. Multi-step classification (supervised classification and spectral disaggregation)
4. Image segmentation
5. Map editing
Land cover classes and number of training
Site selection based on:
• Visual inspection (lab and field)
• Training sites selected from field in China in February 1998
• Sites Georeferenced
• Limited access to some areas
Image segmentation
• Visual inspection indicated speckle
• Distributed without a clear pattern
• Removed using multi-pass, region based image segmentation algorithm
• Segmentation process enlarges regions by merging neighbouring pixels into polygons
Map editing
• Areas of the Delta exclusively agriculture, classified as urban
• Areas at centre of Guangzhou were classified as crops
• Possibly due to atmospheric effects not uniform throughout the image
• Pollution also had an impact
• Single radiometric calibration was applied
• Overall resulted in relabelling 5% of entire image
Accuracy assessment
• Conducted using validation data independent of the training data
• 496 2x2 pixel sites
• Stratified random sampling
• 151 sites analysed in the field
• 345 analysed in the lab (at least two analysts)
• Analysis made without knowledge of each analysts choice of class
Discussion
• Agricultural class main source of confusion, due to diversity and different crop types
• Multi-crop fields, terracing and small field sizes produce different textures and tones
• Generate heterogeneous surfaces
• Harvested rice fields essentially are bare soil areas, thus confusion with construction sites
• 1988 – 1996 experienced unprecedented scale of land conversion
• 1905km2 converted to urban. Increase of 364%
• 1988 2.67% of study area was urban. 1996 almost 10% of study area changed to urban
• ¼ of new urban areas were natural vegetation or water
• 151km2 of water converted to agriculture.
Conclusions
• Conceptual model composed of spectrally diverse land-covers provides good frame work to infer land-use change from land-cover
• Accuracy assessment was essential
• Unprecedented rates of change
• Urbanization rates of 300%
• Economic growth which has directly improved living standards
• Most conversion is from agriculture to urban areas thus has potential serious implications on regional food supply and biogeochemistry
References
• Seto, K.C., Woodcock, C.E., Song, C. Huang, X., Lu, J. and Kaufmann, R.K. (2002). Monitoring Land-Use change in the Pearl River Delta using Landsat TM. International Journal of Remote Sensing, 23(10): 1985-2004
• TERRASERVER (2006) [Online]. http://www.terraserver.com/