Original article Influences of human activities and agriculture on groundwater quality of Kayseri-Incesu-Dokuzpınar springs, central Anatolian part of Turkey Hatim Elhatip Æ Mustafa Afşin Æ llkay Kuşçu Æ Kadir Dirik Yakup Kurmaç Æ Murat Kavurmacı Abstract Human activities and agriculture have had direct and indirect effects on the rates of contamination of groundwater in the Incesu-Dokuzpınar spring area. Direct effects include dissolution and transport of excess quantities of fertilizers with associated materials and hydrological alterations related to irrigation and drainage. Indirect effects may include changes in water–rock reactions in soils and aquifers caused by increased concentrations of dissolved oxidants, protons, and major ions. Agricultural activities have directly or indirectly affected the concentrations of a large number of inorganic chemicals in groundwater, for example NO3, N2, Cl, SO42, H+, K, Mg, Ca, Fe, Cu, B, Pb, and Zn, as well as a wide variety of pesticides and other organic compounds. For reactive contaminants like NO3, it is recommended that a combination of hydrochemical and environmental-tracer analytical approaches might be required to resolve changing inputs from subsequent alterations as causes of concentration gradients in groundwater. The water type of Dokuzpınar springs is mainly Na–Mg–Ca–Cl– HCO3. Note that the water types of the springs were directly related to the hydrogeochemical properties of outcrops at the study area. Thus, the high concentration of Ca2+ and HCO3 is mainly related to the high CO2 contents in the marbles, whereas the high Na concentration arises from the existing syenite, volcanic ash, basalt, and clay units, although the I_ ncesu-Dokuzpınar springs cover most of the drinking and irrigation water demands of this area. The high concentrations of NO3 and NaCl show that the area around the springs is continuously being contaminated by untreated sewage and agricultural wastes, especially during dry periods. Therefore, this approach is based on the vulnerability studies of the catchment area, determination of the transfer time of the pollutant, and the water-bearing formations of I_ ncesu-Dokuzpınar springs. Vulnerability in this study is defined as the intrinsic hydrogeochemical characteristics of an aquifer, which may show the sensitivity of groundwater to be contaminated by different human activities. Keywords Dokuzpınar Springs Æ Human activities Æ Agriculture Æ Contamination Æ Turkey Introduction and objectives Received: 7 October 2002 / Accepted: 28 January 2003 Published online: 10 April 2003 ª Springer-Verlag 2003 H. Elhatip (&) Æ Y. Kurmaç Aksaray Engineering Faculty, Environmental Eng. Dept., Niğde University, 68100 Aksaray, Turkey E-mail: [email protected] Tel.: +90-382-2150953 Fax: +90-382-2150592 M. Afşin Æ l. Kuşçu Æ M. Kavurmacı Aksaray Engineering Faculty, Geological Eng. Dept., Niğde University, 68100 Aksaray, Turkey K. Dirik Faculty of Engineering, Geological Eng. Dept., Hacettepe University, 06532 Ankara, Turkey 490 Environmental Geology (2003) 44:490–494 I_ ncesu is a province of Kayseri City in the central Anatolian part of Turkey (Fig. 1). The study area lies between latitudes 3830¢ and 3900¢ and longitudes 3500¢ and 3636¢. Kayseri-I_ ncesu has a wet climate with cold and heavy rain in winter and hot summers. The research area comprises different volcanic rocks from Paleocene to Paleo-Quaternary age that have been highly effected by a series of fault zones and reflects different hydrogeological characteristics. Occurrence of springs in the project area is mainly related to tectonism and Erciyes volcanism. The I_ ncesu-Dokuzpınar springs (I_ DSp) emerge from basalt rocks. The whole area of the springs is covered by volcano-sedimentary rocks. Note that the previously mentioned waters discharge upwards along fault lines after leaching the pervious water-bearing formations (Fig. 2). DOI 10.1007/s00254-003-0787-0 Original article Fig. 1 Location map of the study area The main objectives of this study are: to evaluate the influences of human activities and agriculture on groundwater quality of Kayseri-Incesu-Dokuzpınar springs, to utilize the hydrogeochemistry of the main aquifer that recharges the springs, and to evaluate the factors that control the rate and sources of pollutant hazards in the study area. A general view of the springs is given in Fig. 3. The degradation of groundwater depends on the pollution load and the behavior of pollutants as well as the geological and hydrogeochemical factors that control the flow and dispersion. The evaluation of these factors in the most populated areas around Kayseri-I_ ncesu is the subject of the present work. Knowledge of the susceptibility of groundwater to pollution is important to identify remedies and establish the water quality and environmental protection according to TSE (Turkish Standard Institute 1997). Man’s use and reuse of water for domestic, industrial, and agricultural purposes in the overpopulated regions result in the discharge of liquid or solid wastes with different kinds of contaminants into the geological environment. As a result, groundwater quality is seriously stressed. Hydrogeochemistry of the springs Results of the hydrochemical analysis is given in Table 1. The main water type of I_ ncesu-Dokuzpınar springs is Na–Mg–Ca–Cl–HCO3. The water type of the springs was directly related to the hydrogeochemical properties of outcrops at the study area. Thus, the high Na concentration arises from the existing syenite, volcanic ash, basalt, and clay units that exist in the study area. The Ca/Mg, Ca/Na and SO4/Cl ratios, and base change index decrease from the recharge area downwards to the discharge area. This reduction showed that the duration of water-rock contact, depth of groundwater flow pattern, and the travel time increased (Appelo and Postma 1992). The periodic variation in temperature, pH and electrical conductivity (EC) values, and concentrations of individual ions in the water samples from the study area, are graphically illustrated in Fig. 4. A periodic general uniformity in chemical composition exists, which is related to conditions of sources and rate of recharge at the outlet points of the I_ ncesu-Dokuzpınar springs. The general changes in the EC values of groundwater from the spring area are periodically compared with the higher ion concentration changes during the dry and wet seasons. At the end of the dry periods (October), addition of salts may lead to an increase in EC and NaCl values and may cause chemical reactions between the Na and Ca ions during ion exchanges. Also, the high concentrations of most ions in the groundwater probably result from surface leaching during irrigation and from contamination by sewage. Environmental Geology (2003) 44:490–494 491 Original article Fig. 2 Geological map of the study area and its vicinity Fig. 3 General view of the I_ ncesu-Dokuzpınar springs 492 Environmental Geology (2003) 44:490–494 Influence of human activities and agricultural contaminants on water quality The phrase ‘‘agricultural contaminants’’ in this study refers to chemicals whose concentrations in groundwater seem to be higher than they would be in the absence of agricultural activities, although they might not necessarily come directly from applied artificial substances. Use of the word ‘‘contamination’’ is meant to imply that human activities have caused an increase in the flux or concentration of a constituent, but not necessarily that the change has been harmful. The major contaminant considered in this paper is NO3), which is the most abundant, mobile, and persistent agricultural contaminant in many shallow groundwaters. Irrigation, farming, and waste drainage in the study area have altered groundwater fluxes and flow patterns. Agricultural contaminant loads in recharging groundwater have resulted in well-known societal problems related to drinking-water quality and ecological effects of ground- Original article Table 1 Hydrochemical analysis of I_ ncesu-Dokuzpınar springs Parameters T pH EC Na K Ca Mg HCO3 SO4 Cl Cu Fe Zn Pb Mn Ni Cd Cr B SiO2 NO3 NO2 PO4 NH3 NH4 Units (C) – (lS/cm) (mg/l) (mg/l) (mg/l) (mg/l) (mg/l) (mg/l) (mg/l) (mg/l) (mg/l) (mg/l) (mg/l) (mg/l) (mg/l) (mg/l) (mg/l) (mg/l) (mg/l) (mg/l) (mg/l) (mg/l) (mg/l) (mg/l) 25 March 2000 12 7.3 377 41.00 5.50 18.00 11.50 103.82 11.88 70.90 0.532 0.103 0.14 0.127 0 0 0 0.022 1.615 5.675 16.01 0.01 0.151 0.068 0.4 16 October 2000 13 6.9 530 62.2 6 27 18 122 14.44 95.72 0.824 0.125 0.16 0 0 0 0 0.01 1.821 7.568 18.24 0.015 0.272 0.1 0.68 25 May 2001 12.5 7.1 320 78.4 7 24.5 17.75 158.2 16.47 120.5 0.639 0.1 0.1 0 0 0 0 0.015 1.652 5.962 16.96 0.01 0.184 0.094 0.5 Fig. 4 Periodic changes in ion concentrations water discharge to surface-water bodies. In addition, agricultural contaminants have caused substantial changes in groundwater geochemistry and water-rock interactions, which have received somewhat less attention. Global trends indicate that agricultural effects on the hydrochemical cycle will continue to be important topics of research in the future (Hem 1970). The main sources of nitrate in the study area include: nitrate from the application of fertilizers in irrigation and from detergents in untreated waters. The common fertilizer applied liberally throughout the irrigation district is (NH4)2SO4. Through a nitrification process in the presence of oxygen, ammonium is transformed into nitrates according to the following reaction (Freeze and Cherry 1979). Fig. 5 Periodic changes in the heavy-metal and nutrient concentrations 2O2 þ NHþ 4 ¼ NO3 þ H2 O Greater mineralization is generally associated with the higher nitrate concentrations of the I_ ncesu-Dokuzpınar springs. The high nitrate concentrations may occur due to the leaching of NO3 from fertilizers and biocides during irrigation of agricultural land and leakage from overloaded sewage networks are sources of NO3 pollution (Fig. 5). Thick volcanic ash with clay layers in the study area probably prevents or at least retards the introduction of pollutants to the aquifer. The contrasting transport behavior of chemicals like NO3 and various pesticides makes the design of management strategies for minimizing their effects on ecosystems complicated. However, a high nitrate content and significant mineralization in the groundwater are probably due to contamination of the recharge to the aquifer by irrigation drainage, deteriorated sewage networks, and septic tanks (APHA, AWWA, WPCF 1989). Some other inorganic constituents of groundwaters that are present in agricultural additives include Cl, K, Ca, Mg, and a variety of minor elements. Agricultural sources of some of these elements can dominate natural sources locally. Furthermore, agricultural effects on the recharge fluxes of various ions like NO3 and H+ can cause changes in weathering rates and ion-exchange equilibrium in the subsurface, thereby altering indirectly the concentrations of other constituents in groundwater. These indirect effects have important implications for geochemical studies of water–rock interactions and can represent sources or sinks for a variety of problematic contaminants such as nutrients and toxic trace elements. Finally, estimating the role of human activities on the optimum yields of the springs for certain uses is important for environmental balance and ecosystems. The high NO3, NH3, NH4, and PO4 concentrations in the I_ ncesuDokuzpınar springs reflect the influence of liquid wastes, frequent use of detergents, and widespread farming and stockbreeding around the spring areas. The discharge of liquid wastes that have nutritious organic materials from the surrounding food, textile, and leather factories into the receiver environment causes the Environmental Geology (2003) 44:490–494 493 Original article precipitation of intensive mud deposits and changes the color of these deposits. These wastes have high heavymetal concentration, such as; B, Fe, Cu, Pb, and SiO2. This type of water causes acidic influences at relatively different rates in the discharge environment. Therefore, the amount, distribution rates, and environmental effects of the settlement, agricultural, and industrial waste ‘‘pollutants’’ around the spring area were investigated in detail. Results and conclusions Urbanization activities around Kayseri City affect the groundwater quality in the shallow zones, depending on the hydrological characteristics that control the flow and dispersion of water and contaminants. The groundwater of the Quaternary aquifer in the recharge area of the I_ ncesuDokuzpınar spring has great mineralization, high nitrate pollution, and more depleted heavy metal contents, especially at the outlet points in the downstream side. The thick clay and volcanic ash layers overlying the aquifer in the upstream side have probably retarded the inflow of younger water, which carries pollutants from irrigation drainage and an overloaded sewage network. However, in the downstream side of the I_ ncesu-Dokuzpınar area the aquifer is more vulnerable to pollution. Common agricultural practices have caused substantial increases in the groundwater-recharge fluxes and concentrations of major elements and a variety of other heavy metals. These increases have resulted in a transient agricultural chemical signal in aquifers that have groundwater residence times of decades or more. Some elements are added to the hydrosphere directly as components of fertilizers or other additives, whereas some are associated indirectly with fertilizer loadings or land disturbance through enhanced rates of leaching of natural sources in soils, owing to physical and biological changes and to increased acidity or ionic strength of agricultural recharge. In addition, high fluxes of NH4 and NO3 in recharging groundwater have resulted in unnaturally high concentrations of chemical species released from aquifer materials by oxidation reactions in the saturated zone, because the electron demand of NO3 in agriculturally contaminated recharge is commonly several times higher than that of dissolved O2 in uncontaminated recharge. Recommendations Indirect human activities and agricultural effects on groundwater composition are of geochemical significance and can be useful as tracers of agricultural groundwater in 494 Environmental Geology (2003) 44:490–494 the study area. Although uncertainty and debate still exist about the sources and pathways of NO3 in groundwater recharge, several different types of evidence indicate that excessive applications of artificial fertilizers and manures have contributed substantially to the recharge rate of NO3 in many parts of the world. Agricultural studies on the behavior of N and other important constituents in soils and crops have not been coupled universally with studies that follow the progress of those constituents below the root zone, in groundwater recharge, and through aquifers. In addition to the major constituents commonly associated with agricultural contamination, more work is needed on the indirect effects that agricultural groundwater infiltration and recharge have on water–rock interactions, such as leaching, weathering, and biogeochemical transformations in soils and aquifers, including dissolution and precipitation of toxic or environmentally sensitive elements that are not necessarily included in agricultural additives. Future applications of environmental tracers to agricultural contamination studies should include more sophisticated applications of multiple-tracer analyses to systems with substantial transit times in the unsaturated zone and the saturated zone, and to groundwater mixtures in discharges from wells and springs. Advances in the understanding of complex systems are expected to occur as long-term trends in multiple-tracer data are developed at individual sites, and by the application of more realistic transport simulations for multiple tracers, including agricultural contaminants. Acknowledgements Sincere thanks are extended to the funding group of the project that was provided by the Scientific and Technical Research Council of Turkey (TÜBI_ TAK). I am also grateful to my colleagues Yakup Kurmaç and Murat Kavurmacı, who helped in the field and laboratory work for this project; the reviews of the manuscript were also much appreciated. References APHA, AWWA, WPCF (1989) Standard methods for the determination of water and waste water, 15th edn. APHA publication, 1134 pp Appelo CAJ, Postma D (1992) Geochemistry, groundwater and pollution. Amsterdam Freeze RA, Cherry JA (1979) Groundwater. Prentice-Hall, Englewood Cliffs, NJ, 553 pp Hem JD (1970) Study and interpretation of chemical characteristics of natural water. US Geol Surv Water-Supply Paper no 1473. US Government Printing Office, Washington, DC TSE (TSI) (1997) Drinking water standards (in Turkish). Turkish Standard Institute, Ankara, vol 28, p 97
© Copyright 2026 Paperzz