Recent Advances in Energy, Environment, Biology and Ecology The impact of climate changes on water balance from western Romania using computer tools HALBAC-COTOARA-ZAMFIR RARES Hydrotechnical Engineering Department “Politehnica” University of Timisoara nd 2 Victoriei Square, 300006, Timisoara, Timis ROMANIA [email protected] Abstract: - Global climate is changing and the impacts on water resources can be hardly predicted. Climate change creates variations in water storage and fluxes at the land surface, in storage in soil moisture and groundwater, seasonal snow packs; wetlands and reservoirs, precipitation, runoff and evapotranspiration. This paper will use a program to analyze the impact of climate changes on water balance from western Romania using as input data temperature and precipitation values for a period of 30 years. Key-Words: climate changes, water, Romania, water balance high plain regional climate, hills regional climate and mountains regional climate [1]. The annual average temperatures presents variability depended on the relief forms, with values from 4º - 7ºC (in mountain areas) to 10º - 11ºC. During spring and summer, the dominant air masses are temperate type of oceanic provenience and they bring the most important contribution regarding precipitation volume. In this sense, an obvious example is the flooding from 2005. The cyclones and warm air masses influence from Adriatic Sea and Mediterranean Sea are felt especially during winter by the frozen and solid precipitation missing while during summer are periods with extreme hot temperatures [2]. The precipitation regime has an irregularly character, with wetter years than the average followed by years with very few precipitations. 1 Introduction Climate changes are alterations on long-term of weather components as temperature, precipitation etc. Generally, when we discuss about the impact of climate change, we firstly talk about water. Water is a vital component of our environment, society and is one of the main components of climate changes. The impact of climate change on water is undeniable and is experienced most directly on water availability. Perhaps the most visible direct impacts of climate change on water, relentless in expression and covered area, are land degradation and floods. 2 Climate change influences in water balance The water balance plays a key role in the interactions between climate and biosphere. Water balance, which includes elements as precipitation, runoff, evapotranspiration will not remain unaffected by these shifts induced by climate change. Climate change alters precipitation patterns leading to fundamentally differences in comparison with a past situation. Evapotranspiration also presents variations across a landscape due to temperature, humidity, wind and vegetation cover. 3 Climate in Western Romania For Timiş County, characterized by a moderated continental temperate climate with Mediterranean influences, and with periods in which the climate in unpredictable, were identified 4 major regional climates as it follows: low plain regional climate, ISBN: 978-960-474-358-2 Fig. 1 Geographical map of studied area [3] The analyzed area covers the Aranca River’s hydrographic basin, a plain area having a slope 106 Recent Advances in Energy, Environment, Biology and Ecology - Calculation of linear regression, non-linear, simple and multiple regression and polynomial; - To assess whether a data series fits to a series of distributions: normal, log-normal, gamma, logPearson Type III, Gumbel and log-Gumbel. If the data set fits a distribution, to calculate such flows or design rainfall with a return period or given a certain probability of occurrence; - Calculate from the curve of seasonal variation or duration curve, design events with certain probability; - Conduct analysis and calculate storm intensities from rain data; it also allows the calculation of the average rainfall for the simple average method, Thiessen polygon and isohyets; - Calculation of maximum flow with empirical and statistical methods; - Calculation of evapotranspiration using Thornthwaite, Blaney-Criddle, Penman and Hargreaves as well as water balance calculations. around 0.30 ‰, meaning that the plain is almost horizontal. Aranca Plain is low subsidence plain of meadow with microform beds and abandoned meanders, surface drainage channels, fluvial and anthropogenic mounds. Climate falls under temperate continental climate with mild winters and significant amounts of rainfall. The summer is defined by unstable weather with showers and thunderstorms. The hydrography of the analyzed area is the result of the combined action of climatic factors, morphology and geology. The region Aranca groundwater contributes to excess soil water, but only up to a depth of 2 m; starting from a 2.3 m depth, the groundwater has no influence on soil, but contributes to his water supply during drought. The channel water supply is from precipitation, groundwater springs and fountains of waters. In terms of soils, we can find in this area large surface with Chernozem, Fluvisols, Vertisols and Pelosols [2, 3]. Climatic data (temperature and precipitation) necessary to be used by Hidroesta program were purchased from Sannicolau Mare. 5 Analysis of climate changes impact on water balance using Hidroesta The analysis was made on a 5 year step, from 1980 until 2012. The evapotranspiration values used in calculations were obtained based on Thornthwaite method. The results are presented in the following figures: Fig. 2 Hydrographic map of analyzed area [2] 4 Hidroesta Hidroesta is a program for hydrological and statistical calculations applied in hydrology. Hydrological studies require substantial analysis of hydrometeorological information; this information may consist of rainfall data, flow, temperature, evaporation. The data collected represent only raw data, but if they are organized and analyzed properly, provide the hydrologist a useful tool that allows him to take the proper decisions. HidroEsta is a tool that facilitates and simplifies the laborious calculations, and the process of analyzing the wealth of information that must be performed in hydrological studies [4]. HidroEsta allows: - The calculation of statistical parameters for clustered and nonclustered data; ISBN: 978-960-474-358-2 Fig. 3 Water balance for Sannicolaul Mare (1980) area obtained with Hidroesta Fig. 4 Water balance for Sannicolaul Mare (1985) area obtained with Hidroesta 107 Recent Advances in Energy, Environment, Biology and Ecology Fig. 5 Water balance for Sannicolaul Mare (1990) area obtained with Hidroesta Fig. 9 Water balance for Sannicolaul Mare (2010) area obtained with Hidroesta 6. U.S.G.S. model This model analyses the allocation of water among various components of the hydrologic system using a monthly accounting procedure based on the methodology originally presented by Thornthwaite. As input data, this model requires mean monthly temperature (T, in degrees Celsius), monthly total precipitation (P, in millimetres), and the latitude (in decimal degrees) of the location of interest (is needed for the computation of potential evapotranspiration (PET)) [5, 6, 7, 8]. Actual evapotranspiration (AET) results from potential evapotranspiration (PET), Ptotal, soilmoisture storage (ST), and soil-moisture storage withdrawal (STW). Monthly PET is estimated from mean monthly temperature (T). PET represents the climatic demand for water relative to the available energy. PET is calculated with Hamon equation [9]: Fig. 6 Water balance for Sannicolaul Mare (1995) area obtained with Hidroesta PET = 13.97 ⋅ d ⋅ D 2 ⋅ Wi where d is the number of days in a month, D represents the mean monthly hours od daylight in units of 12 hours and Wi is a saturated water vapor density term (g/m3). For Wi we have the following relation [9, 10]: Fig. 7 Water balance for Sannicolaul Mare (2000) area obtained with Hidroesta Wi = where T is the mean monthly temperature in degrees Celsius. In the situation when Ptotal for a month is less then PET, then AET is equal to Ptotal plus the amount of soil moisture that can be withdrawn from storage in the soil. Soil-moisture storage withdrawal (STW) linearly decreases with decreasing ST such that as the soil becomes drier, water becomes more difficult to remove from the soil and less is available for AET. If Ptotal plus STW is less than PET, then a water deficit is calculated as PET–AET. If Ptotal exceeds PET, then AET is equal to PET and the water in excess of PET replenishes ST. When ST is greater than STC, the excess water becomes surplus (S) and is eventually available for runoff [7, 8, 10]. Fig. 8 Water balance for Sannicolaul Mare (2005) area obtained with Hidroesta ISBN: 978-960-474-358-2 4.95 ⋅ e 0.062⋅T 100 108 Recent Advances in Energy, Environment, Biology and Ecology 7. Results obtained with Geological Survey model U.S. Fig. 14 Water balance components for Sannicolaul Mare (1990) area obtained with USGS model Fig. 10 Water balance components for Sannicolaul Mare (1980) area obtained with USGS model Fig. 15 Water balance components for Sannicolaul Mare (1990) area obtained with USGS model Fig. 11 Water balance components for Sannicolaul Mare (1980) area obtained with USGS model Fig. 16 Water balance components for Sannicolaul Mare (1995) area obtained with USGS model Fig. 12 Water balance components for Sannicolaul Mare (1985) area obtained with USGS model Fig. 17 Water balance components for Sannicolaul Mare (1995) area obtained with USGS model Fig. 13 Water balance components for Sannicolaul Mare (1985) area obtained with USGS model ISBN: 978-960-474-358-2 109 Recent Advances in Energy, Environment, Biology and Ecology Fig. 18 Water balance components for Sannicolaul Mare (2000) area obtained with USGS model Fig. 22 Water balance components for Sannicolaul Mare (1985) area obtained with USGS model Fig. 19 Water balance components for Sannicolaul Mare (2000) area obtained with USGS model Fig. 23 Water balance components for Sannicolaul Mare (1985) area obtained with USGS model 7. Discussions and conclusions First of all we should take a look at the main 2 factors used in these analyzes: precipitation and temperatures. Fig. 20 Water balance components for Sannicolaul Mare (2005) area obtained with USGS model Fig. 24 Precipitation variations for 1980-2012 Fig. 21 Water balance components for Sannicolaul Mare (2005) area obtained with USGS model Fig. 25 Temperature variations for 1980-2012 ISBN: 978-960-474-358-2 110 Recent Advances in Energy, Environment, Biology and Ecology bringing additional support in covering the necessary water volumes. Concluding on the used models, I can say that Hidroesta is a good program for analyzing the water balance but still needs some improvements. First of all, this model doesn’t work with negative temperatures which may represent a disadvantage. On the other side, the lack of an English version (the program has an interface in Spanish) reduce its spread and use. U.S.G.S model is a better model because it offers the possibility to analyze more components of water balance, especially the runoff values which, in agricultural sector, has a major impact if is not managed properly. U.S.G.S. works with both positive and negative values which offer a better accuracy. Fig. 26 Variation of PET and P-PET (1980-2010) It can be observed that if the temperatures are presenting a continuous increasing trendline, precipitations reached a maximum volume around 2005. The period between 2000 and 2008 was a relative rainy one which succeeds to support the water requests from agriculture (especially) but also from other domains. Unfortunately, in some years, these rains were concentrated resulting in significant flows which overrun the floodplains capacity. After several discussions with farmers and specialists involved in land reclamation and improvement works, this positive precipitation trendline is somehow a returning to a previous situation from 1960 – 1980, when these volumes were very important especially during summer season for establishing a balance between plant demands and available water resources. The driest period is the one between 1985 and 2005. We can consider that during these 20 years, climate changes had the most significant impact. It can be explained once through the existence of an important industry activity in western part of Romania especially from chemical sector. After 2000, many companies, big polluters, were closed. Even the temperatures are continuing to present an increasing trendline, the difference between P and PET remains above the levels which we have 30 years ago. The water balance presents, during the last 10 years, a good improvement especially in the second half of a year where, in the past, we had the worst situation. For many years, precipitations were concentrated between January and May while the autumn crops faced water scarcity at different levels or, in some isolated cases, heavy rains which affected their development. We can say that climate changes impact on water balance from western Romania can be divided in two periods: one between 1985 and 2005 when we had climate conditions with aridization specific and the second period, started after 2005 with high temperatures but also with significant precipitations ISBN: 978-960-474-358-2 References: [1] Ianoş Gh., Puşcă I., Goian M., Banat Soils, Natural Conditions and Fertility, Mirton Publishing House, Timişoara, 1997; [2] Nedelcu R., The impact of hydroameliorative works and other sources on transborder waters quality from Banat hydrographical space, PhD Thesis, „Politehnica” University of Timisoara, Timisoara, 2007; [3] The Monograph of Sinnicolaul Mare City, http://sannicolaumare-monografie.blogspot.ro/ (accessed 04/03/2013); [4] Bejar V.M., HidroEsta, Editorial Tecnologica de Costa Rica, 2006; [5] Thornthwaite C.W., An approach toward a rational classification of climate, Geographical Review, Vol. 38, 1948, pp. 55–94; [6] Mather J.R., The climatic water balance in environmental analysis, Lexington, Mass., D.C. Heath and Company, 239 p., 1978; [7] McCabe G.J., Wolock D.M., Future snowpack conditions in the western United States derived from general circulation model climate simulations, Journal of the American Water Resources Association, Vol. 35, 1999, pp. 1473–1484; [8] Wolock D.M., McCabe G.J., Effects of potential climatic change on annual runoff in the conterminous United States, Journal of the American Water Resources Association, Vol. 35, 1999, pp. 1341–1350; [9] Hamon W.R., Estimating potential evapotranspiration, Journal of the Hydraulics Division, Proceedings of the American Society of Civil Engineers, Vol. 87, 1961, pp. 107–120; [10] McCabe G.J., Markstrom S.L., A monthly water-balance model driven by a graphical user interface, U.S. Geological Survey Open-File report 2007-1088, 2007, 6 p. 111
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