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Poster Sessions
  • Session 1
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  • ACRS 1999


    Environment
    A Methodology in Detailed Environment Mapping for Viral Disease Survey

    Classification of the area by the results of types/states and heterogeneity approaches
    The Spectral based organisation is then re-arranged by the textural one through a GIS modelling. Which ends up in a spatial organization potentially composed of a maximum number of 36 classes.



    Final Spectral and Textural based organization

    Intrinsic Remote Sensing Labelisation of Classes
    To give a first stage remote sensing label to the classes, they are analysed following their spectral and disturbance level behaviours.

    The spectral behaviours are studied through the knowledge brought by the Tasseled Cap (Crist and Cicone, 1984) model applied to the facts furnished by the actual data resulting from the classification process.

    The disturbance is studied by building knowledges concerning their relative levels, very low to very high, through statistical analysis.

    The results are presented in the table below.

    Water Vegetation Urdan
     
    Spectral
    Texture
    123456
    Homogeneous
    not disturbed
    1112131415161
    2122232425262
    3132333435363
    4142434 44 54 64
    Heterogeneous
    very disturbed
    5 15 25 35 45 55 65
    616 26 36 46 56

    Table 1 : Remote sensing Class Labels.
    Reading of the types: 66 is class 6 of the spectral based organization at the level 6 of the “disturbance organization”.


    The last step of labelisation, is done through a survey and questionnaire, whose sampling frame is dictated spatially and statistically by the modeled reality obtained from the previous remote sensing approach. This last step is aiming at the providing of common understandings and meanings to the classes, plus very precise answers to very clearly defined questions.

    Conclusion
    Current results obtained in the study of the Dengue show that it is now possible to identify and localize precisely environmental indicators and factors of viral diseases. Furthermore it is also now possible to predict estimates of where the viral diseases could probably and spatially burst, and at what level of incidences. Next developments would concern the introduction of dynamics and time, and enlargement of the study of factors and indicators to social, economical, cultural and ecological parameters.

    References
    • Ahearn, S.C., De Rooy, C., 1996. Monitoring the effect of dracunculiasis remediation of agricultural productivity using satellite data. International Journal of Remote Sensing, Vol. 17, No. 5, 917-929.
    • Andrianasolo H., 1990. Réduire l’incertitude sur unr région rurale: une approche relevant de l’estimation de surface, à travers une modelisation reposant principalement sur les données satellitaires, sous contrainte d’opérationnalité. In : Représentation, Modelisation, Développement – Agropolis/GIS – Systèmes Energétiques – Utilisation de l’Espace – ACCT, pp49-81.
    • Beck LR, Rodrigues MH, Dister SW, Rodrigues AD, Rejmankova E, Ulloa A, et al., 1994. Remote sensing as a landscape epidemiologic tool to identify villages at high risk for malaria transmission, Am J Trop Med Hyg., 51: 271-80.
    • Crist, E.P., Cicone, R.C., 1984. Application of the Tasseled Cap concept to simulated TM data. Photogrametric Engineering and Remote Sensing, Vol.50, 343-352.
    • Gesler, W., 1986. The uses of spatial analysis in medical geography: a review. Soc. Sci. Med, 23, 963-973.
    • Glass GE, Schwartz BS, Morgan JM III, Johnson DT, Noy PM, Israel E., 1995. Environmental risk factors for Lyme disease identified with geographic information systems. Am J Public Health, 85: 944-8.
    • Wood, B.L., Beck, L.R., Washino, R.K., Hibbard, K.A., Salute, J.S. (1991). Estimating high mosquito-producing rice fields using spectral and spatial data. International Journal of Remote Sensing, Vol.13, No.15, 2813-2826.
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