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GISdevelopment > Proceedings > ACRS > 1999


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Sessions

Agriculture/Soil

Water Resources

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Measurement and Modeling

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Forest Resources

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Oceanography/Coastal Zone

Topics Including Education

Hyper Spectral Image Processing

Image Processing

Geology

Environment

GIS

Global Change

Airborne Remote Sensing

Poster Sessions
  • Session 1
  • Session 2
  • Session 3
  • Session 4
  • Session 5
  • Session 6



  • ACRS 1999


    Poster Session 1
    Analysis of Water Quality Pattern near the Lake Hinuma using Passive Image Data

    The principal component analysis
    The principal component analysis is tried on the variable of the pelitic sediment (3). Primary main component (Z1) and second main component (Z2) that exceeded 80% at the accumulation contribution ratio were adopted. It was divided into 3 groups by the plotting of the main component score on the Z1....Z2 plane. The ratio of coarse grain sediment of the sand and silt is big for first group Gs1, and there are features of which all nitrogen and moisture are comparatively small. Second group Gs2 and third group Gs3 has the contrary property to the first group Gs1.

    It is the characteristic of second group Gs2 that mud quantity, all nitrogen and moisture, etc. are big. These of third group Gs3 are comparatively small. These group Gs1, Gs2 and Gs3 are shown in Figure-4.


    Fig.4 Result ofthe principal component analysis


    Satellite image and the classification result

    The utilization image
    As satellite image data from the passivity sensor, Landsat·TM data in the Ibaraki Prefecture area in Japan is used. This image data are extracted on 24 Apr. 1994, and it is a scene of path 107-row35 and 0% cloud amount.

    CCT value of water area.
    Training area of assumed 6 sites was selected from water area in the image analysis district. The difference of mean CCT value of these training area affects to the evaluation of the classification. The almost equal class of the mean value of CCT value is arranged, and Table-1 is made.

    Table-1 Distribution of the band data in water areas
    water areaBand 1 Band 2Band 3Band 4Band 5 Band 6Band 7
    NO.192.535.5 34.120.214.1117.76.7
    NO.298.140.140.124.818.5122.38.8
    NO.392.738.940.125.519.4128.18.6
    NO.494.330.939.726.619.1130.18.6
    NO.597.340.241.126.519.1128.48.7
    NO.697.741.143.329.220.9131.79.3

    Next, there is seldom difference of CCT value of band 1 and band 7 as the result of examining the CCT value with band data of each class. Then, the classification was carried out next selected bands.

    1) Band 1, 2,3, 4, 5, 7                   3) Band 2, 3, 4, 5
    2) Band 2, 3, 4, 5, 6

    Thematic map preparation by these band variables is carried out by remote sensing analysis system of RSIPS[4].

    The image classification result
    Waters in Lake Hinuma, Nakagawa River and coastal zone have been classified into six kinds. Clustering processing of a round robin inspection needs a long time. So the clustering uses sampling mesh data instead of all pixel data of study area. The sampling mesh data number was made to increase from 250, and test of the clustering was carried out. The sampling mesh data number was increased till about 450 and classification result was stabilized. The selectivity of superscription variable is examined from the classifi-cation result of waters. Referring to the pattern of this classification result, the high similarity training district selected 12 classification items from study area (4). In making this training district to be the supervised data, the classification was applied to the satellite image data for the purpose of water area in the lake Hinuma, Nakagawa River and coast. This result is shown in Figure-5. The classification map was output by the application of maximum likelihood method (MLHM). Figure-6 is this classification result.

    Discussion
    Sea surface area is divided into 2 layers when the relation of the classified pattern of the water system of LANDSAT satellite image data by remote sensing technique and water depth. The lake Hinuma water and the Nakagawa River water were distinguished. It is possible to distinguish the lake Hinuma water to suicidal drowning and effluent area and lake area of Shishido river. The complicated pattern property is shown near the center in the lake, and the classification result changes by selection position of the training area, and stabilizing pattern property is not shown. It is difficult to under-stand the complicated pattern property near the center of the lake by satellite image data analysis in a time.

    Conclusion
    The analysis becomes easy, if the part of business work analyzed from existing material and drawing and field study data is simplified by the new technique. Until now, the situation of surficial extension and distribution pattern has been easy to understand by diagrammatizing characteristic group got from the principal component analysis of the 3, 4 chapter. This pattern situation may be replaced to the investigation of the remote sensing from the sky (5) under the expectation of the superscription. The classification technique of remote sensing was applied to image datum. This result is as follows. Shishido river effects category is classified as class A of Lake Hinuma water system. It was also possible to find its boundary. This is correspondent to group a1 shown in the water quality data analysis. The Hinuma watershed is interpreted as effect category class B of the coastal water.

    This is corresponded to group a3 of the water quality data analysis. The Hinuma watershed is understood as effect category class B of the coastal water. This is corresponded to group a3 of the water quality data analysis. It is not possible to show clear boundaries near the center of the lake for the complicated pattern property such as class C and D. This is corresponded for group a2 of the water quality data analysis and group of Gs2 and Gs3 of the soil analysis. The pattern in the sea water area in the coast is classified into the 2 classes. Class F is the deep water, and class E is the shallow water depth area in the effect category of the running water of Nakagawa River.

    Reference.
    • National Astronomical Observatory (1998): Chronological Scientific Table’98, Maruzen,pp.662-663.
    • Yukio Asuma, Horie, M. Ishii, T. Miura, K. and Ohshima, K(1998):Environment Resources of Ibaraki Prefecture Hinuma, Region Integrated Lab. of Ibaraki Univ., pp.1-21.
    • Noboru Ohsumi (1989): Statistical Data Analysis and Software, Education Promotion Association of Broadcasting University, pp.116-136.
    • Takashi Hoshi(1979) : Processing System “USAS” of MSS Data from an Aircraft and It’s Application, Published in the Proc. of JSCE ,No.285, pp.69-83.
    • D J Maguire, M. F Goodchild and D. W Rhind (1991):Geographical Information Systems: Principles and Applications,,Longman Group UK Limited, Sec.14.
    • Kazuhito Tanii and Takashi Hoshi (1999) : Useful of unsupervised classification residual image using RSIPS, Proc. 58th annual conference of IPSJ,1-D,pp.2-17~18.

    Fig.5 The classification result of Ward's method



    Fig.6 Classification result of MLH method

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