The role of daily precipitation

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The role of daily precipitation interpolation for the SWAT model performance across different spatial and temporal scales MATEUSZ SZCZEŚNIAK MIKOŁAJ PINIEWSKI TOMASZ BEREZOWSKI WARSAW UNIVERSITY OF LIFE SCIENCES WULS SGGW

Default SWAT method Based on the Nearest Neighbour For each subbasin the amount of precipitation is taken from the nearest station Missing values replaced by SWAT built in Weather Generator (WXGEN)

Objectives Do selected spatial interpolation techniques can improve the performance of the SWAT model in predicting flows in differrent spatial and temporal scales?

Case studies Case one: 11 meso scale (119 to 3935 km 2 ) sub catchments lying in the Sulejów reservoir catchment finished and published* Case two: 80 catchments (500 to 3000 km 2 ) Vistula and Odra Basins ongoing study * Szcześniak, M., & Piniewski, M. (2015). Improvement of Hydrological Simulations by Applying Daily Precipitation Interpolation Schemes in Meso Scale Catchments. Water, 7(2), 747 779.

Sulejów reservoir catchment Part of the Pilica River catchment, located in the central Poland Total area 4,928 km 2

Meteo inputs 49 stations, mainly precipitation 30 years of daily data

Used methods of spatial interpolation Aside of the default SWAT method (Def), three methods were used: Thiessen Polygons (TP) Inverse Distance Weighted (IDW) Ordinary Kriging (OK) SWAT CUP SUFI 2 algorithm was used as a tool for evaluation of the results

Ten slajd z różnicami w interpolacji? Mean yearly precipitation (30y) a Def b TP c IDW d OK Example daily precipitation a Def b TP c IDW d OK

SUFI 2 calibration parameters Name Lower limit Upper limit Definition ESCO.hru 2 0.7 1 Soil evaporation compensation factor EPCO.hru 2 0 1 Plant uptake compensation factor SOL_Z().sol 1 0.4 0.4 Depth from soil surface to the bottom of layer SOL_AWC().sol 1 0.4 0.4 Available water capacity of the soil layer SOL_BD().sol 1 0.4 0.4 Moist bulk density SOL_K().sol 1 0.9 2 Saturated hydraulic conductivity HRU_SLP.hru 1 0.3 0.3 Average slope steepness ALPHA_BF.gw 2 0.9 2 Baseflow alpha factor GW_DELAY.gw 2 50 400 Groundwater delay time GWQMN.gw 2 0 1000 Threshold depth of water in the shallow aquifer required for return flow to occur GW_REVAP.gw 2 0.02 0.2 Groundwater "revap" coefficient RCHRG_DP.gw 2 0 0.3 Deep aquifer percolation fraction CN2.mgt 1 0.15 0.15 Initial SCS runoff curve nr for moisture condition II SURLAG.bsn 2 0.3 3 Surface runoff lag coefficient SLSUBBSN.hru 1 0.3 0.3 Average slope length (m) CH_N2.rte 2 0.01 0.1 Manning's "n" value for the main channel CH_N1.sub 2 0.01 0.1 Manning's "n" value for the tributary channel ( ) SMTMP.bsn 2 2 2 Snow melt base temperature TIMP.bsn 2 0 1 Snow pack temperature lag factor SNOCOVMX.bsn 2 0 40 Minimum snow water content that corresponds to 100% snow cover Note :1 parameter multiplied by 1+r, where r is a number between lower and upper limits, 2 parameter replaced by the new value from the range.

Results Box plots of PBIAS across all 11 flow gauging stations for different interpolation methods (Def Default version, TP Thiessen Polygons, IDW Inverse Distance Weighted, OK Ordinary Kriging) and different objective function / temporal aggregation combinations (A, B, C, D ). Box plots of selected objective functions across all 11 flow gauging stations for different interpolation methods (Def Default version, TP Thiessen Polygons, IDW Inverse Distance Weighted, OK Ordinary Kriging)

Box plots of percent changes in RMSE across all 11 flow gauging stations for different interpolation methods (Def Default version, TP Thiessen Polygons, IDW Inverse Distance Weighted, OK Ordinary Kriging) and different objective function / temporal aggregation combinations (A, B,, C, D ). Scatter plots of changes in different obbjective functions and various catchment descriptors for relationships with significant correlation (at significance level 0.05

Conclusions from Sulejów Case the most complex OK method outperformed other methods in terms of NSE, whereas OK, IDW and TP outperformed Def in terms of br 2, regardless of temporal aggregation The difference between TP, IDW, OK and Def was spatially variable. Part of this variability was attributed to catchment properties. Spatial interpolation can improve the model simulations however various methods should be tested as the results tend to be catchment specific.

Vistula and Odra Basins Part of the ongoing CHASE PL project Vistula River basin area 194 10 3 km 2 Odra River basin area 119 10 3 km 2 Vistula the 2nd largest river basin in EU, Odra the 5th

3 4 5 2 Vistula and Odra: 2nd and 5th largest river basins in EU 1

Development of gridded temperature and precipitation datasets for modelling overview Item Minimum and maximum temperature Precipitation Domain Poland + Vistula and Odra basins Data sources IMGW PIB Polish stations DWD German and Czech stations ECAD, NOAA NCDC Slovak, Ukrainian and Belarusian stations Preprocessing Quality assessment Quality assessment Richter correction for precipitation undercatch Interpolation method Kriging with elevation as external drift Library R gstat Time frame 1951 2013 Resolution 5 km grid in the projected coordinate system PUWG1992 Output format.tiff files (one file per variable per day) Cross validation All stations, for each day. Both temporal and spatial scale SWAT input Aggregation at subbasin level Combination of Universal Kriging and Indicator Kriging (for wet day probability estimation)

Temperature and precipitation stations network

Annual variability of available data Cross validation results: standardized RMSE Precipitation Median range 0.7 0.8, with more than 85% of RMSE values not exceeding one standard deviation Range: 300 700 Negative correlation with the numer of available stations Errors depend on the density of the observation network

Catchments used in study Odra outlet Vistula outlet

Mean yearly precipitation, years 1989 2000

Results Daily KGE Daily KGE Def Kriging Def Kriging Box plot of KGE objective function across all 80 flow gauging stations for Default method Def and Universal Kriging Box plot of KGE objective function across all flow gauging stations (except Lug VVO) for Default method Def and Universal Kriging

Default 30 25 KD 20 15 R² = 0.006 KGE objective function for whole Vistula and Odra catchments Gauge Vistula outlet KGE Default KGE Kriging 0.71 0.76 10 5 0 0.20 0.30 0.40 0.50 0.60 0.70 0.80 0.90 1.00 KGE 30 25 20 Kriging Odra outlet 0.78 0.76 KD 15 10 5 R² = 0.0636 0 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 KGE Scatter plots of KGE and Kernel Density

Conclusions from Vistula and Odra case Further investigation of the used interpolation method is needed