MAPPING THE FLASH FLOOD PRONE AREA IN THE TAITA WATERSHED (ROMANIA) USING TOPOGRAPHIC INDEXES AND HYDRAULIC MODEL

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ICNAR 2014 MAPPING THE FLASH FLOOD PRONE AREA IN THE TAITA WATERSHED (ROMANIA) USING TOPOGRAPHIC INDEXES AND HYDRAULIC MODEL C. Maftei K. Papatheodorou

Outline Research context Research objective Research approach Results and discussion 2

Research context Climate change impact Flood Effects of flood temperature (2002-2012) >1.3 o C (pre-industrial period) spatial and temporal variability of precipitation frequency of extreme precipitation intensity and frequency of river floods in winter and spring (in various regions) N o events (1980-2011) - 3455 N o events in Europe 325 (200 since 2000) No of people killed: 195843 Av. people killed per year:6,753 Economic Damage (bill. US$): 397,333,885 Application of Flood Directive Prepare flood hazard and risk maps Prepare flood risk management plans scenario considered: frequent event (low probability) medium event (medium probability - 100 years) extreme event (high probability - 1000 years). Flood elements provided flood extent, WS profile, WS depth, WS velocity 3

Research objectives Re-examine the flood mapping methodology Propose a method to assess the spatial extent of flooding USGS 1988 NFIP and FEMA APFM Morphologic and Hydraulic coupled models 4

Research approach Flood problem in the Dobrogea region Status and analysis of observations Mapping the flood prone area Evaluate results 5

Flood mapping methodology Flood mapping production according USGS-1988 comprehensive intermediate approximate 1.detailed 2. historical 3.analytical 4.physiographic 5.reconnaissance statistical analysis Flood mapping production according with FEMA - 2002 regional method Empirical model RR model Watershed model determining T-year discharge general examination of the stream to approximate the area that would be inundated hydraulic model no gauged basin? yes flood map delineation regression equation, index-flood relation, area-altitude relation, rational model, unit hydrograph simulation model flood frequency analysis no 3 4 determining T-year water-surface profile or depth? yes Chezy and the Manning formula The T-year profile is obtained by adding T-year depths to the channelbed profile 2 which method are using? 1 develop a profile for the historical flood on the basis of high-water marks determine the frequency of the historical flood define ratios of observed flood depths to depths for discharges of various recurrence intervals determine the adjustment needed to convert from the historical profile to the T-year profile flood routing dynamic equation of gradually varied flow 6 developing a flood-boundary map transferring altitudes from a water-surface profile to a map

Dobrogea region Location Geo-morphology Climate Temperature Precipitation Hydrology 7

Flood problem in the Dobrogea region No Town, village Date Characteristics Damages 1. Garlița 1963;1971-2. Casian 24.09.1968 442mc/s* 3. Lumina 1967-30 household teared down and animals taken away by the floods Households and crops destroyed, human lives lost Flooded households and destroyed 4. Runcu 11.06.1985 h apa=1.60 m Households destroyed and 5 deaths 5. Baia 16.07.1967 - Households and gardens flooded 6. Constanța Households flooded in 01.07.1992;28 rainfall >200 mm/12 h the Western area, 3,29.08.2004 deaths Households and 7. Nuntaşi/Nuntasi 01-11.09.1999 32.mc/s (fig. ) gardens flooded, 1 death 8. Cheia 9. Costineşti 10. 11 12 Casimcea/Casimce a Cheia/Casimcea Cuza Voda/Agi Cabul Negureni, Valea Marea 02.- 04.09.1999 22-23.09.2005 30-31 V 2002 8-9 VIII 2002 - Flood coming from upstream, at Biruinta registeredt>300mm/2 4 h 398mc/s* 384mc/s* 2-4 IX 1999 57,8 * 2-7 IX 1999 26,8 * 13 Albesti 30-31 V 2000 153 mc/s* 14 15 16 Sacele, raul Valea Sacele Saraiu, raul Topolog Biruinta,/ Valea Biruinta 8-9 VIII 2002 45mc/s* 2-20 VII 2005 214 mc/s* 20-25 IX 2005 131 mc/s* 17 Urluia/V.Urluia 14-19 VI 1992 10.6mc/s* Households and gardens flooded, school Damages to the railway, access roads, restaurants, households in Schitu Households and gardens flooded, access bridge damaged no no 8 18 Taita/Taita 3.03.1985 56.6mc/s

Study area and Taita catchment area 591 km 2 elevation ranges 261m 10 tributaries part of North Dobrogea Plateau the main source of supply precipitation 74% The hydrometric data are collected in two hydrometric stations: Hamcearca Satu Nou Vegetation >33% forest 9

data base In this study the series of annual maximum stream flow, covering the period 1968 (1965)- 2010 have been used. 10

Mapping the flood prone area Flooding mapping proposed yes gauged basins? no Observed data Topographic Land use Historical flood event flood frequency determining T-years discharge Hydraulic model river profiles cross section roughness coeff. DEM Geomorphological model Roughnes map Historical map Flood parameters WS profile WS depth Flood map hazard Calibrate 11

Flood frequency: frequent event (low probability -10 years) 50 years medium event (medium probability - 100 years) extreme event (high probability - 1000 years). Pearson III distribution 30mc/s 56mc/s 74mc/s 192mc/s Hydraulic model ArcGIS Topographic Map Contour Map DEM Hydrology HEC GEORAS Set of RAS geometry: river system banks cross section RAS RUN HEC RAS Set of HEC RAS results: water surface level velocity discharge in cross section Geomorphological model Topographic Wetness Index (TWI) SAGA Wetness Index (SWI) Calculation Models Set of maps: Flow direction Flow accumulation BH Delineation Generate GIS export file Result prepocessing Ras Mapping Generate GIS export file Delineation Flood plain 12

Geomorphological Model Topographic Wetness Index (TWI) & SAGA Wetness Index (SWI) Calculation Model TWI As: Accumulation per unit contour length β: slope Software Used Beven, K. and Kirkby, M. : A physical variable contributing area model of catchment hydology, Hydrolog. Sci. Bull., 24(1), 43 69, (1979). Moore, I. D., Burch, G. J., and Mackenzie, D. H.: 'Topographic effects on the distribution of surface soil water and the location of ephemeral gullies', Trans. Am. Soc. Agr. Engrs., 31, 1098-1107, (1988). Sørensen R., U. Zinko, and J. Seibert: On the calculation of the topographic wetness index: evaluation of different methods based on field observations. Hydrol. Earth Sys. Sci. Discuss., 2, 1807 1834, European Geosciences Union, (2005). Boehner, J., Koethe, R. Conrad, O., Gross, J., Ringeler, A., Selige, T.: Soil Regionalisation by Means of Terrain Analysis and Process Parameterisation. In: Micheli, E., Nachtergaele, F., Montanarella, L. [Ed.]: Soil Classification 2001. European Soil Bureau, Research Report No. 7, EUR 20398 EN, Luxembourg. pp.213-222, (2002) 13

Geomorphological Model - Results SAGA T.W.I. Software Used Geodetic Reference System: Dealul Piscului 1970/ Stereo 70 Terrain Ruggedness Index Stream Power Index 14 Geodetic Reference System: Dealul Piscului 1970/ Stereo 70 Topographic Wetness Index (TWI)

Results hydraulic model 15 50 years return period 1000 years return period

Comparison of Results 16 Geodetic Reference System: Dealul Piscului 1970/ Stereo 70

Conclusions (1/3) Hydrologic and hydraulic modeling was applied to assess flash flood prone areas delineation and flood hazard, by using widely accepted FFH assessment methodologies. Flash flood prone areas were delineated using the Topographic Wetness Index (based on TOPMODEL) and the SAGA WI geomorphological models. Inundation areas were also delineated using the HEC- RAS hydraulic model by taking into consideration 100 and 1000 years return periods. 17

Conclusions (2/3) Comparison of the results of the different type models used, shows that there is a remarkable convergence in the delineation of the inundation (flooded) area despite the fact that these models have very different input data requirements. Taking into consideration that the geomorfological models have minimal data requirements as the required data are readily available (ASTER DEMs, topographical data), these models can be used to reliably delineate flood prone areas on a regional scale in order to proceed with Risk assessment. At a next stage, hydraulic models can be used especially on site-specific (local) scales in order to accurately estimate the flooding parameters (inunndation area, depth, flood water velocity etc), thus helping make decisions about designing effective preventive measures. 18

Conclusions (3/3) To demonstrate the broad applicability of the selected methodologies, open source software was used to store, process data and create maps. As resulted, Quantum GIS (v.2.1), SAGA GIS (v.2.08) and HEC-RAS can be effectively used to fully apply the proposed methodological approach as they provide very reliable platforms at no cost. Acknowledgments: The research was partially funded by the EU within the context of the Black Sea Basin Joint Operational Programme 2007-2013 19