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Van-Genuchten-Mualem parameters

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1 Van-Genuchten-Mualem parameters
Climate change impacts on the water regime of a brown forest soil Gelybó, Gy., Tóth, E.*, Bakacsi, Zs., Molnár, S., Farkas, Cs. Institute for Soil Sciences and Agricultural Chemistry, Centre for Agricultural Research, Hungarian Academy of Sciences H-1022 Budapest, Herman Ottó út 15. * Abstract In this study the effects of climate change on forest soils has been evaluated with scenario analyses based on mathematical modelling. Meteorological data were originated from the FORSEE database, which provides bias-corrected climate data based on the ENSEMBLES EU project, soil properties data were obtained from the TIM database. The intraannual variability of soil water regime was examined on 18 representative years sampled from the whole period. We concluded that the main annual temperature will gradually increase, although the amount of precipitation will decrease in the near future (A1B55) and increase in the far future (A1B100). The number of days with extreme high precipitation (more than 20 mm per day) will increase, while the number of rainy days will be decreased. Evaporation and transpiration will increase in the near and the far future in both wet and dry years. Material and methods Climate data. Climate data (bias corrected temperature and precipitation) used in this study were obtained from the 1/6 × 1/6 degree resolution FORESEE database (DOBOR et al., 2012) that is based on the results of the ENSEMBLES project. The database provides continuous dataset for the period, characterizing climate variables by one common reference dataset for the past ( ) and eight different climate model runs for the future ( ) considering A1B emission scenario. Results of the RegCM (International Centre for Theoretical Physics) regional climate model were used in model calculation. For average values of past, near future, far future subperiods see Table 1. Figure 1. Geographical location of soil sampling points. Soil data Soil characteristics of the study area were obtaine from the Soil Information and Monitoring System (Várallyay, 2002; Table 2.). We analyzed possible changes in soil water regime for soil profile #E7705 (Figure 1) Table 2. Soil data for the study site ID Depth [cm] Plast. Index SAND SILT CLAY Org. Cont Genetic Soil Type E7705 0-4 40.00 31.87 36.90 31.23 7.52 brown forest soil with clay illuviation 4-29 41.00 28.23 35.85 35.92 1.63 29-79 48.00 27.72 31.12 41.16 0.65 79-129 37.63 29.50 32.87 0.20 42.00 32.51 30.96 36.53 0.24 Table 1. Climate data in the studí period. Modeling The SWAP (Soil-Water-Atmosphere-Plant) model (VAN DAM, 2000) simulates water movement in the unsaturated zone in relation to plant growth for one or more successive vegetation periods. Principally, the model is based on physical equations but also incorporates semi-empirical and empirical relationships. Meteorological, plant and soil data, as well as initial and boundary conditions are required to run the model. We used the SWAT 2.2 model version for our studies. Soil hydraulic functions determining soil water regime are defined according to the Van Genuchten-Mualem analytical expressions. Sample year selection Representative dry, wet and average sample years were selected based on the statistical evaluation of annual total precipitations (RT) in each subperiod. The probability of a year with RT less than a certain amount is shown in Table 1. A year is considered dry, wet and average if RT equals to the lower, upper quartile or the median, respectively (allowing 2% discrepancy). The resulting 2 to 5 years in each subperiod and were ranked based on their Simple Daily Intenzity Index (SDII). Years with the highest and lowest SDII were retained for further analysis (ensuring consideration of precipitation intensity); see Table 4. Table 3. SWAP model parameters Van-Genuchten-Mualem parameters E_7705 A (0-4cm) B (4-29cm) C (29-79cm) D (79-129cm) E ( cm) saturated soil water content WRC (cm3 cm-3) 0.45 0.54 0.49 0.51 residual water content WRS (cm3 cm-3) 0.01 fitting parameters Alpha (cm-1) 0.02 0.04 0.03 n (-) 1.16 1.17 1.98 1.19 1.22 Results Climatologic characteristics Soil moisture regime and soil water balance elements Table 4 Sample years (precipitation) Table 5 Sample years (water balance) Ref A1B50 A1B100 minSDII maxSDII 0.25 (dry) RT 687 674 726 714 760 765 RR1 112 99 121 92 110 SDII 6.1 6.8 6.0 7.76 6.9 8.3 0.5 (average) 811 831 837 841 856 854 149 103 116 105 119 96 5.4 8.1 7.2 8.01 8.9 0.75 (wet) 939 955 917 908 941 943 129 108 135 123 122 7.3 8.8 7.4 7.7 8.4 Ref A1B50 A1B100 minSDII maxSDII 0.25 (dry) EV 165 173 202 172 207 192 TR 417 475 499 410 551 481 DP 11 1 147 2 242 0.5 (average) 195 174 189 212 220 198 479 506 517 599 554 593 3 143 4 12 96 0.75 (wet) 205 209 217 197 570 574 571 681 625 633 79 18 191 127 5 416 Figure 3. Number of days with optimal soil water content Climatology (Figure 2) SDII increases (not significant): precipitation intensity increases, not uniformly distributed through the year Soil water regime Number of days with optimal soil water content (Dopt) will increase in dry years (Figure 3), The change is smaller in average or wet years, The effect of smaller amount of rainfall can be detected in the number of days with optimal soil moisture content in the near future, especially in years with average amount of precipitation. Number of those days when soil moisture content is below the wilting point Dhp shows similar patterns (Figure 4) Soil water balance elements Changes in soil water balance elements will be demonstrated altogether for 18 years representing the studied period (Table 5). In the near and the far future evaporation and transpiration will be increased in both the wet and the dry years as well, which can be explained with the higher amount of precipitation. Values of deep percolation do not show any general tendency. Figure 4. Number of days with soil water content below wilting point Figure 2. Average SDII in the three subperiods References: Dobor, L., Barcza, Z., Havasi, Á., Fodor, N., Preparation of high resolution climate scenarios for agricultural impact analysis in Hungary. (poster) European Geosciences Union, General Assembly 2012, Vienna, Austria, April, 2012 Van Dam., Field-scale water flow and solute transport. PhD thesis Wageningen University, the Netherlands, 167 p. Várallyay, Gy. (2002). Soil survey and soil monitoring in Hungary. In European Soil Bureau - Research Report 9, ESB, Ispra, 139–149. Acknowledgements The research was supported by the Hungarian National Research Foundation (OTKA, Grant No. K , K ), and the CarpathCC and TÁMOP A-1/1/KONV research projects.


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