The study of land use survey
in the tropics using Multi Season and Multi Sensor Remote Sensing data
Yasushi Shimoyama, Izumi
Kamiya, Masanori Koide, Tokio Mizuno Photogram metric research
and development office Geographical survey institute Kitazato -1
Tsukuba,305 Japan
Abstract In the tropics
it is important to employ multi- season and multi sensor data for
continual environmental monitoring and for more accurate land use survey
which copes with the seasonal land cover changes the accuracy of land use
classification using multi season data is controlled by accurate
registration among the image data. Conventionally each image data set is
rectified independently to a standard map coordinate system for
registration purpose .How ever this method causes small registration
method using correlation coefficient must be developed in order to lessen
the small errors.
This study concentrates on the image
registration method for LANDSAT MSS & TM SPOT HRV (XS) and MOS-1 MESSR
it includes following four steps.
- Image overlaying on a display for rough geometric correction
- optimization of sub-pixel differences at a set clipped patch area by
the coefficient between two images.
- calculation of coefficient of affine transformation at local area
whose vertexes consist of the patch area.
- execution of geometric correction at each local area.
This
method improved the registration accuracy land use classification from
these image data sets also showed significantly higher accuracy than those
for a single image this results indicated the significance of employing
multi season and multi sensor data for accurate land use survey.
A Registration Method
- Necessity of image registration
Use of multi season and multi
sensor data is desirable in order to monitor temporal environmental at a
wide area and the achieve accurate land use multi season and multi
sensor data the accuracy of land use classification depends considerably
on that of image registration consequently accurate image registration
is required.
- image registration by data correlation
the image of the
highest resolution was rectified to a map coordinate system to create a
standard image then the rest of the input image were registered to the
standard image
A set of patch area is manually clipped from
points the in order to simplify the search for their conjugate points
the image correlation method was employed to utilize computers and the
realize accurate results with low resolution images in which edges are
not well defined the patch areas were shifted bit by bit to find a point
where the correlation coefficient is largest the interpolation of the
standard image to the grid of registered image.
- Geometric correction
The geometric correction was executed by
the affine transformation by the unit of each local area the
coefficients at each local area were calculated using the residents of
four area are vertexes which consist of conjugate points surroundings of
local area are also corrected by the affine transformation of the
nearest local area Case Study The test site in the
this study is phuket island of Thailand . the specification of the image
data for the case study are as follows :
1 2 3 4 |
SPOT MOS-1 LANDSAT LANDSAT |
HRV-XS MESSR TM MSS |
1,2,3 1,2,3,4 1,2,4,7 4,5,6,7 |
bands bands bands bands |
12.13.1988 02.06.1989 02.04.1989 04.20.1987 | The
standard image data was SPOT HRV data and the other images were registered
to the spot image.
- The correlation coefficients at each patch areas.
The
optimized correlation coefficeients at each patch area are shown at
table 1 the correlation coefficients of highest calculated except for
band 1 of each combination because patch 2,5 and 8 are chose at land
where topographical features are inferior and the other patch areas are
all set at the seashore the correlation of 2,5 and 8 were low.
After the correlation coefficients were computed patch areas are
moved vertically and horizontally by the interval of 0.2 pixel and
optimized reasonable are set where the coefficient of correlation is
largest .
At the surroundings of the optimized position of patch
area this coefficient of correlation changes in table 3 this proves that
the coefficient is dominant around the optimized position and that
residuals can be measured reasonably by the unit of sub pixel.
- the coefficient of correlation of test site.
The affine
transformation was employed to geometrically correct the image data of
the test site to investigations yo accuracy of geometric correction the
changes the correlation coefficients were analyzed in an urban area of
5*k km at the southeast of test site in each combination the
coefficients were so much improved the effect of the image matching
method. Acquisition of training samples and island uses
classification.
- Acquisition of training samples
Training areas were collected
as polygon data with a digitizer by comparing the image displayed on CRT
with the field survey data on this maps training samples were acquired
from the image pixels surrounded by the training areas data.
Table 1 optimized correlation coefficient at
each patch area
|
Optimized correlation coefficient |
Patch area No. |
Between HRV & TM |
Between HRV & MESSR |
Between HRV & MSS |
1 |
0.90 |
0.87 |
0.90 |
2 |
0.76 |
0.79 |
0.53 |
3 |
0.83 |
0.94 |
0.91 |
4 |
0.85 |
0.92 |
0.92 |
5 |
0.87 |
0.91 |
0.70 |
6 |
0.93 |
0.94 |
0.90 |
7 |
0.83 |
0.93 |
0.95 |
8 |
0.75 |
0.88 |
0.87 | Table 2 correlation
coefficient before the registration.
|
HRV |
|
1 |
2 |
3 |
T M |
1 |
0.78 |
0.68 |
-0.49 |
3 |
0.71 |
0.75 |
-0.28 |
4 |
-0.66 |
-0.34 |
0.91 |
7 |
-0.12 |
0.17 |
0.56 |
M E S S R |
1 |
0.72 |
0.53 |
-0.63 |
2 |
0.35 |
0.50 |
-0.03 |
3 |
-0.60 |
-0.28 |
0.86 |
4 |
-0.63 |
-0.33 |
0.73 |
M S S |
1 |
0.76 |
0.49 |
-0.74 |
2 |
0.75 |
0.68 |
-0.53 |
3 |
-0.42 |
-0.08 |
0.72 |
4 |
-0.52 |
-0.23 |
0.73 | Table 3 the changes of
correlations coefficients at the surroundings of the optimized position
of patch area
|
Sift to the column direction |
-0.4 |
-0.2 |
0.0 |
0.2 |
0.4 |
Shift to the row direction |
-0.6 |
0.44 |
0.62 |
0.79 |
0.82 |
0.78 |
-0.8 |
0.46 |
0.66 |
0.85 |
0.86 |
0.80 |
-1.0 |
0.40 |
0.67 |
0.90 |
0.87 |
0.77 |
-1.2 |
0.05 |
0.50 |
0.81 |
0.73 |
0.60 |
-1.4 |
-0.48 |
0.19 |
0.64 |
0.57 |
0.45 | Table 4 Correlation
coefficients after the registration
|
HRV |
|
1 |
2 |
3 |
T M |
1 |
0.81 |
0.71 |
-0.51 |
3 |
0.75 |
0.79 |
-0.31 |
4 |
-0.64 |
-0.31 |
0.94 |
7 |
-0.12 |
-0.22 |
0.56 |
M E S S R |
1 |
0.86 |
0.69 |
-0.62 |
2 |
0.45 |
0.66 |
0.04 |
3 |
-0.31 |
-0.31 |
0.92 |
4 |
-0.68 |
-0.37 |
0.92 |
M S S |
1 |
0.77 |
0.51 |
-0.71 |
2 |
0.65 |
0.63 |
-0.41 |
3 |
-0.50 |
-0.12 |
0.80 |
4 |
-0.62 |
-0.28 |
0.85 | Figure 3
Acquisition of training area
- Land use classification
the maximum likelihood method was
employed for the land use classification of training data .Classified
result is shown in table image data was superior to the other image data
then a single image data was classified independently .How ever when two
image data were simultaneously one reason is that the combination of low
resolution data with high resolution data enables us to perform the
accurate classification considering the surrounding information of the
pixels of high resolution data another reason which may be dominant is
that the data of MSS data acquisition is different from that of the
other data. Table 6, 7 and 8 show the error matrix of classified results
by MESSR , MSS and the combination of MESSR and MSS respectively In the
classification by MESSR urban areas and water areas are accurate and on
the other hand in the classified by MSS land cover of the vegetation is
accurate so in their combination all of land cover class becomes more
accurate consequently this accuracy increase is one of the advantages of
using the multi season and multi sensor remote sensing data.
Conclusion A couple of conclusions of this study are
summarized blow.
- The development o image registration method.
The image
registration method developed in this study significantly reduced the
registration errors among input images also simplified the data
processing of multi season and multi sensor images
- Improvement of the accuracy of the training data classification
The combination of three images acquired in different seasons
improved the accuracy of training data classification .
We are
now improving our method to employ geological data soil data and DTM of
the test site these data are expected to improve the land use
classification of this study. Acknowledgements We
thank TDD Ministry of agriculture and cooperatives Thailand especially mr.
Manu OMAKUPT Ms Promchit TRAKULDIST and Mr Anusorn Chantanaoj for
assisting our field survey.
Table 5 Acuracy of training data classificaion(%)
One sensor |
Two sensor |
Three sensors |
Four sensors |
H |
87.9 |
H+T |
96.0 |
H+T+ME |
98.9 |
H+T+Me+Ms 99.7 |
T |
90.1 |
H+Me |
96.3 |
H+T+WS |
99.2 |
ME |
89.9 |
H+MS |
97.4 |
H+ME+Ms |
98.1 |
MS |
87.9 |
ME+MS |
96.8 |
H+Me+Ms |
99.4 |
|
T+MS |
98.1 |
H........HRV T........TM |
Me+Ms |
98.2 |
ME.....MESSR
T.......M | Table 6 The error matrix of
classified results by MESSR
|
Classified land use |
Urban |
Paddy |
Rubber |
Coconut |
Forest |
Mangrove |
Mine |
Water |
Original Land Use |
Urban area |
560 |
11 |
0 |
11 |
0 |
0 |
21 |
0 |
Paddy |
5 |
556 |
34 |
24 |
0 |
0 |
9 |
0 |
Rubber |
0 |
642 |
14 |
40 |
40 |
0 |
0 |
0 |
Coconut |
4 |
11 |
39 |
91 |
0 |
0 |
0 |
0 |
Forest |
0 |
4 |
6 |
42 |
361 |
22 |
0 |
15 |
Mangrove |
5 |
13 |
0 |
0 |
16 |
485 |
0 |
2 |
Mine |
5 |
0 |
0 |
0 |
0 |
0 |
282 |
0 |
Water area |
20 |
0 |
0 |
0 |
20 |
0 |
2 |
534 | Table 7 The error matrix
of classified results by MSS
|
Classified land area |
Urban |
Paddy |
Rubber |
Coconut |
Forest |
Mangrove |
Mine |
Water |
Original Land Use |
Urban area |
425 |
134 |
0 |
28 |
0 |
0 |
12 |
0 |
Paddy |
65 |
499 |
0 |
2 |
0 |
16 |
0 |
46 |
Rubber |
0 |
5 |
666 |
0 |
25 |
0 |
0 |
0 |
Coconut |
0 |
8 |
0 |
137 |
0 |
0 |
0 |
0 |
Forest |
0 |
0 |
9 |
20 |
418 |
3 |
0 |
0 |
Mangrove |
4 |
8 |
0 |
0 |
0 |
506 |
0 |
0 |
Mine |
8 |
0 |
0 |
0 |
0 |
0 |
279 |
0 |
Water area |
6 |
33 |
0 |
6 |
0 |
0 |
28 |
503 | Table 8 The error matrix
of classifed results by MESSR and MSS
|
Classified land uses |
Urban |
Paddy |
Rubber |
Coconut |
Forest |
Mangrove |
Mine |
Water |
Original Land Use |
Urban area |
580 |
10 |
0 |
1 |
0 |
0 |
12 |
0 |
Paddy |
9 |
615 |
0 |
4 |
0 |
0 |
0 |
0 |
Rubber |
0 |
3 |
689 |
02 |
0 |
0 |
2 |
0 |
Coconut |
2 |
4 |
0 |
139 |
0 |
0 |
0 |
0 |
Forest |
0 |
0 |
0 |
1 |
449 |
0 |
0 |
0 |
Mangrove |
4 |
5 |
0 |
0 |
0 |
509 |
0 |
3 |
Mine |
1 |
0 |
0 |
0 |
0 |
0 |
286 |
0 |
Water area |
1 |
0 |
0 |
0 |
0 |
0 |
5 |
570 | accuracy = 98.2%
|