Abstract
The study area of the Morava River floodplain is situated between the rivers Morava and Kyjovka in the reach from Hodonín to Lanžhot. This experimental area was chosen because during the last 30 years, there has been a serious problem with the frequent occurrence of hydrological extremes, such as floods and droughts. Dry seasons have a very negative impact on the floodplain forest and have been caused mainly by regulation of the Morava River channel in the 1970s. Since flooding in the catastrophic year 1977, a part of this area has served as a polder for flood impact mitigation of the urbanised area of the town of Lanžhot. Management and farming practices have been heavily affected by the enormous economic and ecological damage due to long-term flooding of agricultural land. The purpose of this study is to assess the extent to which the precipitation in the growing season of the dry years 2003 and 2011 was deficient, in comparison with the normal year 2009, through a study of the actual evapotranspiration caused by the significant drought in the Morava floodplain. A similar but converse situation in the wet year 2010 was also analysed, with the aim to show the differences in the components of the water balance equation in the growing seasons of all the extreme years tested here. The daily data from the Kostice climatological station were processed using the WBCM-7 model, where the input parameters were calibrated by the fluctuation of the groundwater table in the control borehole.
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Acknowledgments
Field studies, model improvement, assessment and evaluation have been supported by a grant from the Ministry of Agriculture, the Czech Republic, Project NAZV, QJ 1220033 ‘Optimization of water regime on the Morava river floodplain’.
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Appendix 1
Appendix 1
The explanation of the symbols to Fig. 3 and Fig. 4:
Fig. 3:
RUL (J) = THR (J) − OF (J) − PES (J) (mm)
RUL (J): Positive (filling) or negative (exhausting) functions (mm)
THR (J): Throughfall, OF (J): overlandflow, PES (J): potential soil evaporation
FCUL: Field capacity of upper layer (incl. root zone, in mm)
SMDU (J) = FCUL − WUL (J): Soil moisture deficit (mm)
ΔWUL = WUL (J) − WUL (J-1): Soil moisture content in 1 day (mm)
AES (J): Actual soil evaporation (mm)
J: The day index (−)
Fig. 4:
Resulting equations:
GWS (J) = GWS (J-1) + GWR (J) × (1.0 − (GWS (J-1)) / GWM
GWR (J) = (RECH (J) − AES (J)) × (1.0 − FCLL (J-1) − WLL (J-1)) / FCLL (J-1)
GWF (J) = (GWR (J) × (GWS (J-1) / GWM)
GWT (J) = GWT (J-1) − ((GWS (J) − ((GWS (J) − GWS (J-1)) / POR) / 10.0
BF (J) = BF (J-1) × exp (−1.0 / BK) + GWF (J) × (1.0 − exp (−1.0 / BK))
GWS (J): Groundwater storage (mm)
GWR (J): Groundwater recharge (mm)
RECH (J): Infiltration recharge (from the CN method, in mm)
GWF (J): Groundwater flow (mm)
GWT (J): Groundwater table (m above sea level (m a.s.l.))
GWM: Maximum capacity of active groundwater zone (mm)
FCLL (J): Field capacity of lower layer
BF (J): Baseflow (transformed from groundwater flow, in mm)
WCR (J): Water capillary rise (if groundwater is shallow, in mm)
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Kovář, P., Heřmanovská, D., Hadaš, P. et al. Water balance analysis of the Morava River floodplain in the Kostice-Lanžhot transect using the WBCM-7 model. Environ Monit Assess 188, 74 (2016). https://doi.org/10.1007/s10661-015-5080-7
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DOI: https://doi.org/10.1007/s10661-015-5080-7