Logo GISdevelopment.net

GISdevelopment > Proceedings > ACRS > 2002


1989 | 1990 | 1991 | 1992 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2002
Sessions

GIS, GPS & Data Integration

Land Use Land Cover

Hazard Mitigation and Disaster Management

Photogrammetry

Forestry

Earth Observation from Space

Mountain Environment and Mapping

Data processing, Algorithm and Modelling

Urban Mapping

Hyperspectral Data Acquisition and Systems

AIT: Digital Asia

SAR / InSAR

Very High Resolution Mapping

Soil and Agriculture

Water Resources

Geology / Geomorphology

Education

Ecology, Environment & Carbon Cycle

Infrastructure Planning and Management

Oceanography and Coastal Zone Monitoring

Poster Sessions

Poster 1

Poster 2

Poster 3



ACRS 2002


Land Use/Land Cover


Short- Term change detection with precise geometric correction and sub-pixel land cover characterization of modis


Methodology

1. Examination of geometric correction accuracy
Detecting change in sub-pixel level requires precise overlay between different images. It depends on the accuracy of geometric correction of each image. Firstly, the accuracy of geometric correction done by WebMODIS is examined by pattern matching. NDVI images were used to conduct pattern matching. As matching piece should have a characteristic shape, Oshima and lake Kasumigaura in the study area are selected. NDVI images of these two areas are shown in Fig.3. Correlation coefficients are calculated between the matching piece and 300 x 300 km2 coverage.


Fig.3. NSM images of matching pice (left:Oshima, right:Kasumigaura)


Fig.4. Process of pattern matching

2. Linear mixture modeling
MODIS is one of the few space-borne sensors currently capable of acquiring radiometric data over a broad range of view angles. However, the relatively coarse spatial resolution of the MODIS most often results in measurements of mixed land covers, and thus the pixel unmixing is indispensable. A linear spectral mixture model based on three end-members including vegetation, soil and water is defined by the equations and constraints below


where MODIS ch1 , MODIS ch2 are the MODIS radiance of visible and near infrared channels respectively, and V, S and W are the fractional coverage of vegetation, soil and water respectively. ij a are the end-members and range from 0 to 1.

The number of equations equal to three by incorporating the constraint equation (Eqn.3) in order to calculate the fractional coverage V, S and W. Eqn.3 represents that the sum of three fractions in one pixel equals to 1. By solving three equations (Eqn.1, 2 and 3) simultaneously, we can calculate the fractional coverage of V, S and W.

3. Endmember selection
A mixture model based on three end-members has the simple geometrical interpretation as the triangle whose vertices are the end -members (Fig.5). Since a finite number of hull facets has only finitely many partitions, there are only finitely many simplexes the method can construct, and finding the one with the smallest volume is a combinatorial optimization problem. The triangle is defined to include 95 % of convex hull to eliminate the exceptional noisy pixels. Fig.6 shows the scatter plot for red and near infrared spectral distribution of MODIS image acquired on 10 Mar. 2002. The vertices of the triangle is defined as follows
  • Vegetation : highest value in near infrared reflectance
  • Soil : highest value in red reflectance
  • Water : lowest value in both red and near infrared reflectance.

Fig 5. Relationship between VSW indices end-members triangle for Red-NIR


Fig 6. Scatter plot for Red-NIR on 2002.3.10

4. Change detection model and evaluation of land- cover change
Fractional coverage of vegetation, soil and water will be derived by spectral mixture analysis. In this study, we assume that there is no land cover change between the two scenes. In addition to that, it is assumed that there is mis-registration error of only one pixel between the two images. Using this assumption, a 3 x 3 filter as described hereafter is applied to reduce the errors. The spatial filtering will be applied to the V, S, and W images on 12 Mar. 2002. Fig.7 depicts the algorithm of the spatial filtering. The process is as follows:
  • Select pixel in Image2 in around 9 pixel of (i, j) involved itself, such as minimize difference between the value and other pixel value (i , j) in Image1,
  • The value of pixel (i , j) in Image2 is replaced selected pixel value,
  • All pixel was done by these transaction and get Image2’ .
Then, three filtered images of vegetation, soil and water on 12 Mar. 2002 will be derived from this processing. Land cover change will be evaluated by simple subtraction between the 10 Mar. 2002 and the 12 Mar. 2002 images of each three end -members. The pixel value of subtracted vegetation, soil, and water image measures land cover change.


Fig 7. Filtering algorithm

Results and Discussion

1. Accuracy assessment of geometric correction by WebMODIS
Correlation coefficients were calculated between the matching pieces and the whole images of both MODIS data on 10 Mar. 2002 and 12 Mar. 2002. Fig.8. shows the result of the pattern matching. Best matching points are easily distinguished from the nearby pixels in these four pairs. Best matching points for both Kasumigaura and Oshima were same. This result shows that the accuracy of geometric correction by WebMODIS is high in pixel level.


Fig 8. Result of pattern matching


Table1. RMSE of percentage for filtered and unfiltered image

Page 2 of 3
| Previous | Next |

Applications | Technology | Policy | History | News | Tenders | Events | Interviews | Career | Companies | Country Pages | Books | Publications | Education | Glossary | Tutorials | Downloads | Site Map | Subscribe | GIS@development Magazine | Updates | Guest Book