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Hydrogeochemistry of shallow groundwaters in western coastal area of Korea : A study on seawater mixing in coastal aquifers  

박세창 (고려대학교 지구환경과학과)
윤성택 (고려대학교 지구환경과학과)
채기탁 (고려대학교 지구환경과학과)
이상규 (한국지질자원연구원)
Publication Information
Journal of Soil and Groundwater Environment / v.7, no.1, 2002 , pp. 63-77 More about this Journal
Abstract
Salinization is an important environmental problem encountered in coastal aquifers. In order to evaluate the salinization problem in the western coastal area of Korea, we have performed a regional hydrochemical study on shallow well groundwaters (N=229) collected within 10 km away from the coastline. The concentrations of analyzed solutes are very wide in range, suggesting that the hydrochemistry is controlled by several processes such as water-rock interaction, seawater mixing, and anthropogenic contamination. Based on the graphical interpretation of cumulative frequency curves for some hydrochemical parameters (esp., $Cl^{-}$ and ${NO_3}^-$), the collected water samples were grouped into two major populations (1) a background population whose chemistry is predominantly affected by water-rock interaction, and (2) an anomalous population which records the potential influences by either seawater mixing or anthropogenic pollution. The threshold values obtained are 34.7 mg/l for $Cl^{-}$ and 37.2 mg/l for ${NO_3}^-$, Using these two constituents, groundwaters were further grouped into four water types as follows (the numbers in parenthesis indicate the percentage of each type water) : (1) type 1 waters (38%) that are relatively poor in $Cl^{-}$ and ${NO_3}^-$, which may represent their relatively little contamination due to seawater mixing and anthropogenic pollution; (2) type 2 waters (21%) which are enriched in $Cl^{-}$, Indicating the considerable influence by seawater mixing; (3) ${NO_3}^-$-rich, type 3 waters (11%) which record significant anthropogenic pollution; and (4) type 4 waters (30%) enriched in both $Cl^{-}$ and ${NO_3}^-$, reflecting the effects of both seawater mixing and anthropogenic contamination. The results of the water type classification correspond well with the grouping on a Piper's diagram. On a Br x $10^4$versus Cl molar ratio diagram, most of type 2 waters are also plotted along or near the seawater mixing line. The discriminant analysis of hydrochemical data also shows that the classification of waters into four types are so realistic to adequately reflect the major process(es) proposed for the hydrochemical evolution of each water type. As a tool for evaluating the degree of seawater mixing, we propose a parameter called 'Seawater Mixing Index (S.M.I.)’ which is based on the concentrations of Na, Mg, Cl, and $SO_4$. All the type 1 and 3 waters have the S.M.I. values smaller than one, while type 2 and type 4 waters mostly have the values greater than 1. In the western coastal area of Korea, more than 21% of shallow groundwaters appear to be more or less affected by salinization process.
Keywords
shallow coastal groundwaters; hydrochemistry; seawater mixing; anthropogenic pollution; Seawater Mixing Index (S.M.I.);
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Times Cited By KSCI : 1  (Citation Analysis)
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1 Fritz, S.J., 1994, A survey of charge-balance errors on published analysis of potable ground and surface waters. Ground Water, 32, 539-546   DOI   ScienceOn
2 Lee. D.S., 1987, Geology of Korea. The Kyohak-Sa Pub., 390p
3 Dixon, W. and Chiwell, B., 1992, The use of hydrochemical sections to identify recharge areas and saline intrusions in alluvial aquifers, Southeast Queensland, Australia. Joumal of Hydrology, 135, 259-274   DOI   ScienceOn
4 Gimenez, E and Morell, I., 1997, Hydrogeochemical analysis of salinization processes in the coastal aquifer of Oropesa (Castellon, Spain). Environmental Geology, 29,118-131   DOI   ScienceOn
5 Whittemore, D.O., 1988, Bromide as a tracer in groundwater studies: Geochemistry and analytica ldetermination. National Water Well Association, Proceedings of Groundwater Geochemistry Conference, Denver, Colorado, 1988, 339-359
6 Nadler, A., Magaritz, M. and Mazar, E., 1981, Chemical reactions of seawater with rocks and freshwater-expeiimental and field observations on brackish waters tn Israel. Geochimica et Cosmochimica Acta, 44, 879-886   DOI   ScienceOn
7 Sinclair, A.J., 1974, Selection of thresholds in geochemical data using probably graphs. Journal of Geochemical Exploration, 3, 129-149   DOI   ScienceOn
8 Lee, S.B., Kim, K.Y., Han, S.R. and Hahn, J.S., 1997, The study on the increased causes of chloride (Cl) concentration of the Samyan 3rd pumping station in Cheju Island. Journal of the Korea Society of Groundwater Environment, 4, 85-94. (in Korean)
9 Monterey County Flood Control & Water Conservation Disthct, 1989, Sources of saline intrusion in the 400-foot aquifer, Castroville area, California. Report prepared by D.K. Todd Consulting Engineers Inc., Berkeley, Califomia, 43p
10 Lepeltier, C., 1969, A simplified statistical treatment of geochemical data by graphical representation. Economic Geology, 64, 538-550   DOI
11 Tennant, C.B. and White, M.L., 1959, Study of the disthbution of some geochemical data. Economic Geology, 54, 1281-1290   DOI
12 Magaritz, M. and Luzier, J.E., 1985, Water-rock interactions and seawater-freshwater mixing effects in the coastal dune aquifer, Coos Bay, Oregon. Geochimica et Cosmochimica Acta, 49, 2515-2525   DOI   ScienceOn
13 Mahesha, A. and Nagaraja, S.H., 1996, Effect of natural recharge on sea water intrusion in coastal aquifers. Joumal of Hydrology, 174, 211-220   DOI   ScienceOn
14 Richter, B.C., Kreitler, C.W. and Bledsoe, B.E., 1993, Geochemical techniques for identifying sources of groundwater salinization. CRC Press, New York, 258p
15 Choi, S.H., Kim, Y.K. and Lee, D.Y., 1991, Sea water intrusion in the coastal area of Cheju Volcanic Island, Korea. Journal of the Korean Institute of Mining Geology, 24, 319-327
16 Jeen, S.W., Kim, J.M., Ko, K.S., Yum, B.W. and Chang, H.W., 2001, Hydrogeochemical characteristics of groundwater in a mid-western coastal aquifer system, Korea. Geosciences Journal, 5, 339-348   DOI   ScienceOn
17 Cooper, H.HJr., Kohout, F.A., Henry, H.R. and Glorer, R.E., 1964, Seawater in coastal aquifers, relation of salt water to fresh water. U.S.G.S. Water-Supply Paper, 1613c, 88p
18 Shaw, D.M., 1961, Element distribution laws in geochemistry. Geochimica et Cosmochimica Acta, 23, 116-134   DOI   ScienceOn
19 Custodio, E., 1987, Hydrogeochemistry and tracers in ground-water problems in coastal areas. Studies and Reports in Hydrology, 45, UNESCO, 213-269
20 Choi, S.H. and Kim, Y.K., 1989, Geochemical characteristics of groundwaters in Cheju Island. Joumal of the Geological Survey of Korea, 25, 230-238. (in Korean)
21 Sinclair, A.J., 1976, Applicadon of probability graphs in mineral exploration. Association of Exploration Geochemists, Rexdale, Ont., 95p
22 Sukhija, B.S., Varma, V.N., Nagabhushanam, P. and Reddy, D.V., 1996, Differentiation of paleomanne and modern seawater intruded salinities in coastal groundwaters (of Karaikal and Tanjavur, India) based on inorganic chemistry, organic biomarker fingerphnts and radiocarbon dating. Joumal of Hydrology, 174, 173-201   DOI   ScienceOn
23 Hem, J.D., 1985, Study and interpretation of the chemicalcharacteristics of natural water. U.S.G.S. Water-Supply Paper, 2254, 263p
24 Turekian, K.K., 1977, Geochemical distribution of elements. In Encyclopedia of Science and Technology (4th ed.), McGraw-Hill, New York, 627-630
25 Lee, C.B., Yoo, H.R. and Park, K.S., 1992, Distnbution and properties of intertidal surface sediments of Kyeonggi Bay, West Coast of Korea. Journal of the Oceanological Society of Korea, 27, 277-289