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Assessment of flood risk in Hat Yai Municipality, Southern Thailand ...

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12C. TANAVUD, C. YONGCHALERMCHAI, A. BENNUI AND O. DENSREESEREKULTable 13.Distribution <strong>of</strong> areas susceptible to <strong>flood</strong> <strong>risk</strong> <strong>in</strong> <strong>Hat</strong> <strong>Yai</strong> <strong>Municipality</strong>.that 64.1 ha (50.5%) <strong>of</strong> Rimkuen Community’s land area was subjectto high and very high <strong>flood</strong> <strong>risk</strong> (Table 13).It is important that <strong>Hat</strong> <strong>Yai</strong> <strong>Municipality</strong> publishes hazard and<strong>risk</strong> maps <strong>in</strong> hard copy and distribute them to the communities <strong>in</strong>order to enhance public awareness about the levels <strong>of</strong> <strong>flood</strong> hazardand <strong>flood</strong> <strong>risk</strong> they are likely to face. As <strong>of</strong> today, no municipality<strong>in</strong> <strong>Thailand</strong> has maps <strong>of</strong> this level <strong>of</strong> accuracy and degree <strong>of</strong> detail.4.5 Risk reduction measures.Complete prevention <strong>of</strong> <strong>flood</strong>s through structural measures isalmost a physical impossibility and is uneconomic (Askew, 1991).Properly designed and operated <strong>flood</strong> works, however, can preventor mitigate <strong>flood</strong> damage with<strong>in</strong> physical and economical limits.The application <strong>of</strong> structural mitigation activities, however, mayhave a negative impact on life, property and the natural environment(Ertuna, 1991). For <strong>in</strong>stance, construction <strong>of</strong> levees throughout low-ly<strong>in</strong>g areas without provid<strong>in</strong>g adequate dra<strong>in</strong>age facilitiescan lead to <strong>in</strong>ternal <strong>flood</strong><strong>in</strong>g that adversely affects residents.Levees may also worsen the hazard <strong>in</strong> other locations by divert<strong>in</strong>gwater from one area <strong>in</strong>to another, and may deprive the naturalenvironment <strong>of</strong> critical habitats, such as wetlands. Furthermore,construction <strong>of</strong> large <strong>in</strong>frastructure type projects, such as dra<strong>in</strong>agecanals or diversion channels, to prevent and mitigate <strong>flood</strong> disastersis realized as no longer feasible <strong>in</strong> <strong>Hat</strong> <strong>Yai</strong> <strong>Municipality</strong> due tothe scarcity <strong>of</strong> available land and the impact on the natural environment.Structural mitigation practices therefore should not beviewed as a panacea for all the problems associated with <strong>flood</strong><strong>in</strong>g<strong>in</strong> this municipality. To effectively reduce the <strong>risk</strong> <strong>of</strong> <strong>flood</strong><strong>in</strong>g, analternative approach that focuses on non-structural measures isneeded to supplement exist<strong>in</strong>g structural efforts. Such non-structuralalternatives would not <strong>in</strong>volve major construction and therefore couldhave proportionately less environmental impact (Geipel, 1993).Risk <strong>of</strong> <strong>flood</strong><strong>in</strong>g can be reduced by decreas<strong>in</strong>g hazards, reduc<strong>in</strong>gor elim<strong>in</strong>at<strong>in</strong>g the vulnerability <strong>of</strong> the elements at <strong>risk</strong>, or acomb<strong>in</strong>ation <strong>of</strong> both actions (DeGraff, 1989). Adoption <strong>of</strong> nonstructural<strong>risk</strong> reduction measures, <strong>in</strong>clud<strong>in</strong>g development <strong>of</strong> landuseplann<strong>in</strong>g, <strong>in</strong>stallation <strong>of</strong> <strong>flood</strong> forecast<strong>in</strong>g and warn<strong>in</strong>g systems,adoption <strong>of</strong> preparedness measures aga<strong>in</strong>st <strong>flood</strong><strong>in</strong>g, and cre-

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