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  • Session 1
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  • ACRS 1999


    Poster Session 1

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

    Takashi Hoshi
    Department of the Computer and Information Sciences.
    Faculty of Engineering, Ibaraki University
    Tel (81)-294-38-5133,Fax(81)-294-38-5282,
    E-mail: hoshi@cis.ibaraki.ac.jp
    Kazuhito Tanii
    Graduate School of Science and Engineering, Ibaraki University
    E-mail: tanii@cis.ibaraki.ac.jp

    Abstract
    The lake Hinuma is receiving the effect of the coastal water as it is close to the ocean. Therefore the aquatic environment unlike general freshwater lake is shown. In this research, water quality pattern of the lake Hinuma was analyzed using satellite image data from the passive sensor. This paper describes results of the image classification and the principal component analysis in the Hinuma region.

    Introduction
    Lake Kasumigaura area (167.6km 2 ) is located in the Ibaraki Prefecture of Japan (1), and is taken seriously as a source of the water use, because it is used for the drinking water. In case of Hinuma water system, it is not suitable for drinking and the scale is small, so it is not noticed in comparison with the lake Kasumigaura. The lake Hinuma in Ibaraki Prefecture flows into the coast along the Pacific Ocean from Nakagawa River. The environment of soil, vegetation and crops have changed delicately in the water system in river, lakes and marshes along to the coast in order to receive the influence of the salinity. The utilization of image data of remote sensing has also handled to the result of small-scale from the large scale. Though environment around the lake Hinuma is not very much noticed up to now, at present it should be also noticed in every region. First, this is analyzed by the collection of field study data for the lake Hinuma in Ibaraki Prefecture. Next, the pattern classification is carried out using satellite image data extracted from the passivity sensor. One of the advantages of image data of remote sensing is to make possible to observe simultaneously wide area. This technology is effective for pattern analysis of water current object that changes every moment. Maximum likelihood method of the supervised classification and Ward’s method of the unsupervised classification is used for the classification technique. The results of the pattern classification of satellite image are compared and are examined while result of statistical analysis of this field information is made to reference. Elements of the water quality for the statistical analysis of field information of the lake Hinuma are water temperatures, water depth, turbidity, salinity, dissolved oxygen, COD, etc. Except for these, the variable of clay, silt, sand, moisture, specific gravity and all nitrogen is also used for the statistical analysis in respect of the soil test of the sediment change. The study area of chapter 2, the analysis of water quality data of chapter 3, the sediment of Hinuma of the chapter 4, and analysis method of existing field study data are described. The chapter 5 describes thematic map preparation near the lake Hinuma using the remote sensing technique. Classification pattern of this thematic map examines if there is any relation with the existing result of data analysis.

    The study area
    Shishido river water empties into Lake Hinuma, and it can not be measured the degree of the inflow in the river with the small scale. The runoff from Lake Hinuma flows in Nakagawa River, and then, it flows into the coast. In this reason, the lake water is not used for drinking water in order to include the thin salinity. There is a field of algae in Lake Hinuma, and it is nutritional lake that becomes a field of egg-laying and water fish rearing of the fish. The major features is as follows, area : 9.4km 2 , lake length : 20km, average water depth : 2.1m, water surface altitude : 0m. The water depth observation was carried out using a sound locator and GPS in the early 1997. The geologic profile was made from field study and existing holing materials. The temperature of surface water was measured at 20cm depth from the water surface. Then, water temperature of the low rise water was measured from the lake bed in 20cm place. Turbidity, dissolved oxygen, electric conductivity data except for the water temperature was also measured from the material that sampled water from two points of surface water and lake bed of the superscription in shipboard. Soil test is analyzed by the bottom sediment survey of moisture, water specific gravity and grain size pattern. These data are mainly used for statistical analysis.

    The analysis of water quality data

    The water depth of the lake Hinuma
    To survey the water depth, 150 sites are selected from 9.4km 2 area of the Lake Hinuma, and it was carried out by Mr. Ohshima et al. The water depth contour line was obtained on the basis of this water depth data. This is shown in the map of the 1/20,000 scale (Figure-1).

    The correlation coefficient between water quality variables
    The data of the water surface and bottom by 18 sites in Lake Hinuma was observed in the ebb tide in May 1997. The observing data types are water temperatures, water depth, turbidity, dissolved oxygen, COD, electric conductivity, salinity and transparency. From these, the correlation coefficient between 5 variables of water temperature, water depth, turbidity, dissolved oxygen (DO) and COD was obtained. Correlation coefficients between main variables are as follows (2)
    1. EC-COD and water temperature -DO (0.75³r³0.70)
    2. DO-turbidity (r = -0.63)
    3. water temperature-turbidity and water depth –DO (r=-0.49)
    4. water depth - turbidity, water depth - water tempera-ture, water depth - COD and water depth - EC (0.43³ ½r½ ³0.32)
    5. COD....water temperature (r=0.23)
    6. EC-water, EC-temperature, EC-DO, EC-turbidity and turbidity -COD (0.10³½r½³0.02)

    Fig.1 Water depth map of the Lake Hinuma

    The principal component analysis
    Main component score of surface water and bottom layer water was plotted in the Z1-Z2 plane, because 70% at accumulation contribution ratio of primary main component (Z1) and second main component (Z2) were exceeded. As this result, it is divided into three groups of fresh water effect area:a1, stagnation brackish water:a2, salt water effect area:a3. Figure-2, 3 shows these three groups of a1,a2 and a3 in Lake Hinuma map.


    Fig.2 Samples to plotted in the Z1,Z2 plane




    Fig.3 Groups of a1-a3 in Lake Hinuma


    The sediment of Hinuma

    The soil data analysis
    The measurement of the specific gravity and moisture, and particle size distribution test were carried out after the picking material aired. Then, the element of the statistical analysis was processed by six variables in addition to clay, silt and sand which were the composition element of the soil, in addition to moisture, specific gravity and all nitrogen. It is calculated by the correlation coefficients between six variables of the clay, silt, sand, moisture, specific gravity and all nitrogen.

    Correlation coefficient between soil variables
    The correlation coefficients between main variables are as follows.
    1. clay-silt (r=-0.82), all nitrogen-moisture (r=0.74)
    2. clay-all nitrogen, sand-moisture (r=0.63)
    3. sand-all nitrogen (r=0.58)
    The absolute value on the correlation coefficient between 2 variables except for the superscription was also under 0.5 on anyway.

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