基于Gis的洪水危险性和脆弱性绘图:以西爪哇苏邦Ciasem流域下游的潮汐和河流洪水为例

B. Narendra, H. H. Siringoringo, C. A. Siregar
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引用次数: 3

摘要

Ciasem流域下游的洪水事件被认为是由于流域和红树林覆盖退化而发生的。本文主要以植被和建成区为主要风险因素,研究了潮汐和河流洪水引起的洪水危害和脆弱性。观测的重点是位于苏邦区北部沿海地区布拉纳坎街道muarvillage的Ciasem流域下游。在ILWIS 3.4软件中使用迭代过程绘制潮汐洪水灾害图,在ArcGIS 10软件中使用水文工具(HEC-geo RAS和HEC-RAS)绘制包含高程、坡度和河流特征的河流洪水灾害图。然后利用这些危险图来确定覆盖植被和建筑区域的危险因素。结果表明,以鱼塘为主要风险因素的西部地区开始发生潮汐淹没。当海平面上升到90厘米高度时,定居点就会被潮汐洪水淹没。当河流流量超过160 m /s时,慈溪河开始泛滥,淹没了稻田、鱼塘和居民点。研究表明,鱼塘和水田对洪涝灾害的易损性较高,而居民点和道路对洪涝灾害的易损性取决于建筑材料。通过继续进行土地复垦活动,恢复红树林植被,执行政府关于红树林管理和水产养殖的规定,并认真考虑沿海保护屏障的建设,可以降低洪水灾害风险。
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Gis Based Flood Hazard and Vulnerability Mapping: a Case Study of Tidal and River Floods in Downstream of Ciasem Watershed, Subang-West Java
Flood events in downstream of  Ciasem watershed are believed to occur due to degradation of  watershed and mangrove cover. This paper studies the flood hazard and vulnerability caused by tidal and river flood, mainly on vegetation and built up areas as the main element of  risk. The observation was focused at downstream of  Ciasem watershed, located in MuaraVillage, Blanakan subdistrict, north coastal region of  Subang District. Tidal flood hazard was mapped using iteration process in ILWIS 3.4 software while river flood hazard map was made up incorporating elevation, slope and river characteristics using hydrological tools (HEC-geo RAS and HEC-RAS) in ArcGIS 10 software. Those hazard maps were then utilized to determine element of  risk covering vegetation and built up areas. Result showed that tidal inundation started to happen in the western area dominated by fish ponds as the main element of  risk.When sea level rose up to 90 cm height, settlement areas were experiencing inundation by tidal flood. Ciasem River began to over flowwhen the river discharge exceeded 160 m 3 /sec and inundated the paddy fields, fish ponds and settlements. This study indicated that fish ponds and paddy fields having high vulnerability to the flood event while that of  settlements and roads depend on the construction materials. Flood disaster risk should be reduced by continuing the land rehabilitation activity, restoring mangrove vegetation, implementing government regulations on management and establishment of  aquaculture in mangrove, and carefully considering  the construction of  coastal protection barriers.
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自引率
25.00%
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