Meso Scale Hydrological Modeling for Kedarnath Flood, Uttarakhand

DOI : 10.17577/IJERTCONV4IS03018

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Meso Scale Hydrological Modeling for Kedarnath Flood, Uttarakhand

Dilip Kumar Jha, R K Paswan, S K Dubey

CED, G B Pant Engineering College, Pauri-Garhwal, Uttarakhand

Abstract- The modeling of hydrological processes in meso-scale basins (approximately 101-103 km2; Blöschl, 1996) have become a topic of interest for hydrologists and water resources engineers in the recent past. In meso-scale basins, processes from smaller scales combine in a complex way to produce an integrated response. Heterogeneity in soil, vegetative cover, land use, etc. is present across this scale, making understanding these hydrological processes difficult. Therefore, identifying basin wide areas with the same dominating runoff generation processes is currently a major challenge in runoff generation process research in meso-scale. As this scale is crucial for water management issues, addressing several societal demands, the meso-scale studies are mainly intended for integrated water resource management and long term impact of land-use and climate change over the hydrological response at the catchment scale.

Moreover, the linkage of a distributed hydrologic model with the spatial data handling capabilities of digital elevation models (DEMs) and Geographical Information System (GIS) offer advantages associated with the full utilization of spatially distributed data to analyze hydrologic processes.

The present study attempts to predict the catchment response to extreme floods caused by concentrated monsoon over a geographic domain. For that an extreme flood event occurred in the state of Uttarakhand, India in the year of 2013 have been selected for study. The flood was caused by concentrated cloud burst in Kedarnath in Chamoli district in June, 2013. For the hilly terrains in the upstream of river, physically-based semi- distributed TOPMODEL has been applied.

Keywords: Meso, basin, flood, GIS, TOPMODEL

  1. INTRODUCTION

    The mesoscale hydrologic model is a spatially explicit distributed hydrologic model that uses grid cells as a primary hydrologic unit, and accounts for the following processes: canopy interception, snow accumulation and melting, soil moisture dynamics, infiltration and surface runoff, evapotranspiration, subsurface storage and discharge generation, deep percolation and baseflow and discharge attenuation and flood routing. The model is driven by hourly or daily meteorological forcings (e.g., precipitation, temperature), and it utilizes observable basin physical characteristics (e.g., soil textural, vegetation, and geological properties) to infer the spatial variability of the required parameters. To date, the model has been successfully applied and tested in more than 300 Pan EU basins, as well as India, and USA, ranging in size from 4 to 550,000 km2 at spatial resolutions (or grid size) varied between 1 km and 100 km. Shown below is the model performance for stream flow simulations over the EU basins.

  2. METHODOLOGY

    Uhlenbrook et al. (2004) described the objectives of meso- scale (101-103 km2) modelling as three folds. Firstly, understanding the distributed runoff generation process is a prerequisite and the selected model must capture it. Secondly, the significant variability of atmospheric forces and runoff concentration in the spatial and temporal domain is needed to be included in the model chosen. Lastly, attention should be given to address several water management issues like societal demands as meso-scale modelling can handle it to the appropriate scale. The watershed studied here consists of rivers Alakhnanda and Bhagirathi. Figure 1.1 shows the study area with its location in the Indian map. The total basin area sums up to 1,465 km2. The total watershed was subdivided into 16 sub-basins with area varying from at minimum 121 km2 to at maximum 682 km2. Out of all the sub-basins 10 sub-basins are selected for TOPMODEL simulation and 06 sub-basins are selected for RISE simulation. The models to be used for simulation are selected based upon the land use pattern derived from NDVI product of SPOT VEGETATION sensor imageries and topography from DEM. Rice agriculture dominated areas and plain terrain areas are selected for RISE simulation.

    Figure 1.1: Bhagirathi River Basin

    In order to reduce the effects of topography and solar illumination on the observed radiance two spectral indices are used in the profile instead of band reflectances. The spectral indices are Normalized Difference Vegetation Index [NDVI

    = (NIR RED)/( NIR + RED)] and Normalized Difference Wetness Index [NDWI = (MIR NIR)/( MIR

    + NIR)] (Gao 1996) respectively. The obtained profiles are joined with smooth curves, considering expected changes in the indices. Figure 1.2 shows the estimated profiles of the indices along with rainfall hyetograph, soil wetness conditions and presence of vegetation

    Figure 1.2: The Map shows the input data for the ArcSWAT: Slope data

    Figure 1.3: NDVI and NDWI profiles for soil wetness regions during monsoon season

    In order to carry out correlation analysis, the TI map was georeferenced with the prepared image stacks. With the help of Geographic Information Systems (GIS) modules, thiessen polygons of 28 rainfall gauging stations spreading all over India were generated to calculate total monsoonal rainfall depth of each watershed. Watersheds statistics including watershed area, area covered by TI range and total rainfall depth were extracted and aggregated into river basin scale.

  3. RESULTS AND DISCUSSIONS

    1. Evaluation

      In order to evaluate mapped wetness regions, hydrological simulation results reported from a distributed hydrological model study were considered. The study, based on the SCS- Curve Number method and remotely sensed data, is found to have predicted well clustered wetness regions in the the Ganga basin (Zade et al. 2005). Out of the predicted wetness regions by this model, four regions were chosen to get the temporal profile of the indices.

    2. Comparison with Topographic Index (TI) distribution Brief description of Topographic index

    Topography defines the effects of gravity on the movement of surface and subsurface runoff in a watershed, and,

    therefore influences many aspects of the hydrologic system. It is parameterized as the statistical distribution of the Topographic Index TI = ln (a / tan ), where ln is the Naperian logarithm, a is the upslope area per unit contour length, and tan is the surface slope gradient. The topographic index has been proven to be an important hydrologic modelling component because it reflects the spatial distribution of soil moisture, surface saturation, and runoff generation processes (Beven and Kirkby 1979).

    Comparisons

    Figure 1.4 shows a set of imageries including the FCC [False Colour Composite; red = NIR, green = B3 (red) and blue = B3 (red)] , TI distribution, normal total monsoonal rainfall and retrieved wetness regions for selected three years in and around the Naye River Basin, India. All images are overlaid along with the river. From the maps of wetness regions, it can be clearly observed that the wetness regions were formed mainly in the upstream of the river due to favourable topography and in the downstream due to coastal plain environment. In figure 1.5 it can be seen that area covered by TI range between 6 and 8 are well matching with the monsoonal wetness regions. However, yearly variations of the wetness regions are observed and are also expected due to annual variation of monsoonal rainfall. Average area of the wetness regions in the selected years is found to be in clse agreement with the area covered by the selected TI range. A scatter plot showing fractional area of the wetness regions and TI ranges of 41 watersheds in the Naye River is shown in Figure 1.5. Interestingly, a good correlation between them is found up to total rainfall depth of around 1400 mm.

    Monsoonal soil wetness regions in Naye River Basins

    To understand spatial distribution of the wetness region, yearly area fraction of wetness regions of all watersheds were extracted for all the three years i.e. 1999, 2000 and 2001. This shows yearly variation of the fractions for Naye River Basins.

    FCC IMAGE (2001) SOIL WETNESS REGIONS (2001) WETNESS FRACTION =

    28.49 %

    FCC IMAGE (2000) WETNESS REGIONS

    (2000) WETNESS FRACTION =

    23.96 %

    Therefore, even through parts of watersheds area are covered by high range of TI index indicating prone to wetness, but for lack of sufficient rainfall depth, the regions are found to be dry.

    40

    35

    FCC IMAGE (1999) WETNESS REGIONS

    (1999) 30

    TI range (%)

    WETNESS FRACTION = 25

    21.31 % 20

    15

    10

    5

    0

    R2 = 0.6479

    Rainfall in mm

    <1100

    1100 – 1200

    > 1200

    TOPOGRAPHIC INDEX (TI) MAP

    NORMAL MONSOONAL

    RAINFALL MAP (THIESSEN POLYGON)

    0 20 40 60 80

    Wetness regions (%)

    Figure 1.5: Relationship between fractional watershed area covered by the obtained wetness regions and that by the TI range in 41 watersheds of the River Mahanadi for year 1999

    Figure 1.5 FCC and monsoonal wetness area in years a) 2001,

    b) 2000, c) 1999; d) TI and e) Normal rainfall in and around the Naye River Basin, India with river network basins. A suitable range of TI values have been found out for each river basin by comparing spatial distribution of TI and soil wetness region pattern. In case of the Naye, Mahanadi, Godavari and Narmada Rivers, area fractions of wetness regions and TI range are found to be in close agreement. In these basins, the average normal monsoonal rainfalls are more than 900 mm. The major exception occurs in the Brahmaputra River Basin where temporal and spatial pattern of monsoon storm events are different than that of the other river basins. It is expected that the expected temporal profile of the indices of the monsoonal wetness regions may not represent the same in this basin.

    Figure 1.6: Temporal profile of NDVI and NDWI of the soil wetness regions located in the Naye River basins

    This table shows the fraction of monsoonal wetness regions in major Indian River basins, in comparison with corresponding area covered by TI range and

    total monsoonal rainfall

    River Basins

    Estimated soil wetness regions (%)

    Average % of 3 years

    Suitable Range of TI

    % of basin area covered by TI range

    Total normal monsoonal rainfall (mm)

    1999

    2000

    2001

    Naye

    15.62

    17.27

    9.91

    14.27

    8-10

    15.32

    947.69

  4. CONCLUSIONS

    This chapter has demonstrated a mapping approach by which the retrieval of monsoonal soil wetness region can be feasible using high temporal satellite data in optical range. The derived soil wetness regions are found to have a significant correlation with the topographic index range and total rainfall depth which are the prime control factors in their formation. From correlation analysis, a significant proportion of the mapped wetness is observed in naye river basins .Therefore, the wetness region can be used for calibration and validation of Meso-scale hydrological models in these river basins.

  5. REFERENCES

  1. J. G. Arnold, D. N. Moriasi, P. W. Gassman, K. C. Abbaspour, M. J. White, R. Srinivasan, C. Santhi, R.D. Harmel, A. van Griensven, M.

    W. Van Liew, N. Kannan and M.K. Jha, 2012. Swat: Model Use, Calibration, And Validation Transactions of the (ASABE) American Society of Agricultural and Biological Engineers, Vol. 55(4): 1491- 1508, ISSN 2151-0032.

  2. J. G. Arnold, R. Srinivasan, R. S. Muttiah and J. R. Williams, 1998. Large area hydrologic modeling and assessment Part I: Model development. J. Am. Water Resour. Assoc. 34(1):7389.

  3. D. K. Borah and M. Bera , 2002. Modeling the Big Ditch Watershed in Illinois and Studying Scaling Effects on Water and Sediment Discharges, the American Society of Agricultural and Biological Engineers, St. Joseph, Michigan.

  4. D. K. Borah and, M. Bera, 2003. Watershed-scale hydrologic and nonpoint- source pollution models: Review of mathematical bases. Trans. ASAE 46(6):1553-1566.

  5. V. T. Chow, D. R. Maidment and L. W. Mays, 1998. Applied Hydrology, McGraw-Hill International Editions Civil Engineering Series, New York.

  6. D. Khare, R. Singh and R. Shukla, 2014. Hydrological Modelling Of Barinallah Watershed Using Arc-Swat Model, International Journal of Geology, Earth & Environmental Sciences, Vol. 4 (1) pp. 224-235, ISSN: 2277-2081 (Online).

  7. D. N. Moriasi, J. G. Arnold, M. W. Van Liew, R. L. Binger, R. D. Harmel, and T. Veith, 2007. Model evaluation guidelines for systematic

    quantification of accuracy in watershed simulations. Trans. ASABE 50(3): 885-900.

  8. J. E. Nash and J. V. Sutcliffe, 1970. River flow forecasting through conceptual models: Part I. A discussion of principles. J. Hydrol. 10(3):282-290.

  9. S. L. Neitsch, J. G. Arnold, J. R. Kiniry, R. Srinivasan and J. R. Williams, 2002. Soil and Water Assessment Tool (SWAT) User's Manual, Version 2000. Blackland Research Center, Grassland, Soil and Water Research Laboratory, Agricultural Research Service: Temple, TX, USA.

  10. H. Noor, M. Vafakhah, M. Taheriyoun and M. Moghadasi, 2014. Hydrology modelling in Taleghan mountainous watershed using SWAT. Journal of Water and Land Development. No. 20 p. 1118.

  11. T. Taffese and B. Zemadim, 2014. Hydrological modeling of a catchment using SWAT model in the upper Blue Nile Basin of Ethiopia E3 Journal of Environmental Research and Management Vol. 5(5). pp. 87-91.

  12. J. V. Tyagi, S. P. Rai, N. Qazi and M. P. Singh, 2014. Assessment of discharge and sediment transport from different forest cover types in lower Himalaya using Soil and Water Assessment Tool (SWAT), International Journal of Water Resources and Environmental Engineering ,Vol. 6(1), pp. 49-66.

  13. Valdiya, K. S. (1985) Accelerated erosion and landslide prone zones in the Central Himalayan region. In: Environmental Regeneration in Himalaya (ed. by J. S. Singh). The Central Himalayan Environmental Association, Nainital, 12-5.

  14. Singh G., Ram Babu, Narain P., Bhushan L. S. & Abrol, I. P. (1990) Soil erosion rates of India. In: Proc. Int. Symp. On Water Erosion, Sedimentation and Resources Conservation (Dehradun, India), 32-38.

  15. Srivastava, R.N., and Ahmad, A., 1979, Geology and structure of the Alaknanda valley, Garhwal Himalaya: Himalayan Geology, v. 9, pp. 225 254.

  16. Landslide dammed lakes in the Alaknanda basin, Lesser Himalaya: causes and implications. Current Science, v. 93(4), pp. 568 574.

  17. Chakrapani, G.J. and R.K. Saini (2009). Temporal and spatial variations in water discharge and sediment load in the Alaknanda and Bhagirathi Rivers in Himalaya, India. Journal of Asian Earth Sciences 35 (2009) 545553.

  18. Abbas, N and Subramanian, V. (1984), Erosion and Sediment transport in the Ganges River Basin , India, Journal of Hydrology, 69, 173-182.

  19. Jain, S.K. (2008). Impact of retreat of Gangotri glacier on the flow of Ganga River. Current Science, 95(8), 10121014

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