Stable isotope (2H, 18O and 87Sr/86Sr) and hydrochemistry monitoring for groundwater hydrodynamics analysis in a karst aquifer (Gran Sasso, Central Italy)
Introduction
Optimum protection and management of groundwater resources in karst areas is a priority objective (European Commission, 1995) in both industrialised and developing countries. Fissured carbonate aquifers host huge resources of high-quality groundwater. They also feed springs that are often used as sources of drinking water or that give rise to wetlands of high environmental value (Bradford and Watt, 1998). These springs or wetlands may be part of protected areas, as in this study.
Reconciling environmental protection with human needs requires an accurate and up-to-date assessment of available resources, based on hydrogeological studies. The availability of resources is influenced, in part, by anthropogenic factors (Custodio, 1997): water exploitation and construction work, such as the Gran Sasso motorway tunnel in Central Italy (Monjoie, 1975, Massoli Novelli and Petitta, 1997, Celico et al., 2004), may interfere with the natural hydrogeological setting.
Often, hydrogeological studies are not sufficient to shed light on the groundwater hydrodynamics of carbonate karst environments, since groundwater also flows through fractures and karst conduits. As described in this study, this knowledge gap can be bridged using hydrogeochemical investigation methods, some of which are based on stable isotopes, such as 18O, 2H and 87Sr/86Sr (Banner et al., 1994, Han and Liu, 2004, Johnson et al., 2000, Jorgensen and Banoeng-Yakubo, 2001, Kattan, 1993, Kattan, 2001, Katz and Bullen, 1996, Marfia et al., 2004, Walraevens and Cardenal, 1994, Thomas and Rose, 2003).
Isotope-based methodologies have become well established in the hydrological community for water resource assessment, development and management, and are now an integral part of many water quality and environmental studies (Clark and Fritz, 1997, Cook and Herczeg, 1999). These methodologies usually rely on “tracing” either isotope species naturally occurring in water (environmental isotopes) or on isotope tracers intentionally introduced into them (UNESCO, 2000).
Unlike the stable isotopes of 18O and 2H in water that have long been used in hydrology (Craig, 1961, Bison et al., 1989, Gonfiantini, 1978), Sr isotopes do not measurably fractionate in nature. Groundwater acquires dissolved Sr: (i) in its recharge area, through infiltration and percolation processes; (ii) along its flowpath, through dissolution or ion exchange with minerals. Hence, 87Sr/86Sr ratios give insight into water–rock interaction processes (Naftz et al., 1997). Various authors (Banner et al., 1989, Dogramaci and Herczeg, 2002, Frost and Toner, 2004, Katz and Bullen, 1996, Petelet-Giraud et al., 2003, Peterman and Stuckless, 1992, Barbieri and Sappa, 1997, Barbieri and Morotti, 2003) demonstrated the advantage of using Sr isotopes as tracers in hydrogeological applications.
Hydrogeochemical and isotope analyses can test and fine-tune a conceptual hydrogeological model. Furthermore, monitoring changes in stable isotopes over time and in space can give a better understanding of aquifer recharge and spring discharge that are essential for defining groundwater hydrodynamics. In addition, monitoring of stable isotopes proves to be a useful tool when urgent land planning decisions are to be made, such as those concerning conservation and management of water resources, as well as assessment of the quality of water for human use (Miroladov and Marjanovic, 1998).
Section snippets
Hydrogeological setting
The study area is the Gran Sasso massif (about 800 km2 wide and with an elevation of 270–2912 m a.s.l.), a carbonate ridge consisting of Meso–Cenozoic units belonging to slope-to-basin lithofacies. The sequence has evidence of tectonic movements due to the Apennine orogenesis, such as overthrusts and successive extensional faults. The massif holds a regional aquifer, with high values of recharge (700 mm/a with respect to 1100 mm/a of precipitation) due to joints, faults and karst features. The
Methodology, sampling and analytical procedures
To obtain detailed information about groundwater flowpaths and spring recharge areas and to better understand the above-described hydrogeological setting (see Fig. 1), 3 spring water sampling surveys were conducted in 2001 (January, April and November), collecting data on in situ physico-chemical parameters and carrying out chemical analyses of main components and stable isotopes. Samples were collected directly from the spring outlets. During the January 2001 survey, all 21 identified springs
Major ions
As shown in Fig. 2, groundwater samples were classified by analysing their main groups of cations and anions and by determining their reaction values (relative percentages). All sampled waters were classified as of Ca++ − Mg++ type (Chebotarev, 1955, Appelo and Postma, 1993), in line with the interpretation of a common origin from the Gran Sasso carbonate aquifer. Nonetheless, some of the waters had more pronounced Ca++ + Mg++ characteristics (groups B, C, D, F and, partially, A),
Discussion
The results of hydrogeochemical and isotope analyses are consistent with the assumed conceptual model of groundwater flowpaths in the massif (Fig. 1). The integrated monitoring technique, adopted in this study, offers clues for a more in-depth understanding of the regional hydrodynamics, based on observed changes of the monitored isotopes over time and in space.
The Gran Sasso aquifer contains an active groundwater flow system that is supported by high recharge rates (about 700 mm/a) (Boni et
Conclusions
Qualitative groundwater circulation models based on water budgets can be enhanced through the use of chemical and isotopic tracers, particularly in karst aquifers. In the studied fractured karst aquifer, groundwater hydrogeochemistry of the main components was consistent with the proposed division of the springs into 6 groups, showing an increase in dissolved solids, mainly Ca++ and , along groundwater flowpaths from the aquifer core to its boundaries. Groundwater chemistry also was
Acknowledgements
The Authors thank the Ministry of Universities and Scientific Research – MIUR (“Ambiente terrestre” project – “Cluster C11b” subproject – Law Decree no. 720/99) for its financial support, “Consorzio di Ricerca Gran Sasso” for its useful assistance, GEOKARST (Trieste, Italy) for δ2H and δ18O analyses, Dr. Giuseppina Benedetti for major element chemical analyses and E. Di Biasio for the chemical preparation of samples analysed by mass spectrometer (VG-54E).
The authors are indebted to Z.E.
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