The Fushë Kuqe costal aquifer is a typical confined alluvial aquifer, located in northwestern Albania. The aquifer medium consists of alternating and discontinuous layers of water-bearing gravel and sand with silt-clay impermeable layers giving to aquifer a multilayer character. Along the Mat River the aquifer seems to be continuous, whereas at distances 1.5 -2 km from the river two to four or more aquifer layers appear separated by clayey layers. The transmissibility of the aquifer is generally high in the central part of the plain, on both sides of Mat River, where it is about 4000 to 8000 m²/d, and gradually decreases to about 500-1000 m²/d at the northern and southern periphery of the aquifer (Eftimi, 2003). The aquifer recharge occurs mainly through water infiltration from the River Mat gravelly bed in the North, and from Droja river in the South, while its natural discharge proceeds to the Adriatic sea.
Based on chloride and TDS content in groundwater, an advancement of sea water intrusion into aquifer fresh water was revealed. The direction of sea water wedge from coastal southwestern sectors towards Gorre and Fushe Kuqe, where pumping station are located (Cenameri and Beqiraj, 2016), favors the opinion that it was caused by a decrease of groundwater pressure due to the high groundwater pumping. An increase of chloride content in groundwater through time was found, which means that sea water intrusion towards the fresh aquifer water is still advancing and is caused by both intensification of groundwater pumping for public water supply and by the private drilling of artesian private wells (Cenameri and Beqiraj, 2016).
By using Simpson ratio (SR) (Todd, 1959) and Jones ratio (JR) (Jones et al., 1999) for investigating seawater intrusion in Fushe Kuqe aquifer, it was recently found that most of groundwater sample fall in the fresh water (SR<0.5; JR>0.86) category as it could be expected for shallow wells (<50m deep) which tap the first aquifer (Eftimi, 2003). Only two wells that tap the second (90m deep) and third aquifer (>150m deep) in the near shore line, show high (3.8 and 7.55) SR values and low (1.0 and 0.8) JR values, respectively.
The δ18O and δ2H values vary within a narrow (-6.78 to -7.96 and -41.86 to -50.53, for 18O and 2H, respectively) range and do not correlate with salinity as it could be expected when a single source of TDS and Cl exists. The lack of correlation between chloride and δ18O indicates that the brackish groundwater is not formed by the mixing in of sea water (Kumanova et al, 2014). In fact, the δ18O and δ2H values do not indicate any enrichment toward sea water isotopic composition.
REFERENCES
Cenameri S., Beqiraj A., 2016. Assessment of seawater intrusion in Fushe Kuqe aquifer, Albania. Bulletin of the Geological Society of Greece. L/2. Proceedings of EGE 2016, Thessaloniki, Greece. 665-661.
Eftimi R. 2003. Some consideration on seawater-freshwater relationship in Albania coastal area. In: Coastal Aquifers Intrusion Technology: Mediterranean countries, J.A.Lopez-Gaeta, J.De Dios Gomez, J.A. dela Orden & G. Ramos, L. Rodrigues editors. IGME Proceedings, 239-250.
Jones, B.F., A. Vengosh, E. Rosenthal, and Y. Yechieli, 1999. Geochemical investigations, in Bear, Jacob, and others, eds., Seawater intrusion in coastal aquifers—Concepts, methods and practices, Dordrecht, The Netherlands, Kluwer Academic Publishers, p. 51–71.
Kumanova, Xh, Marku, S, Fröjdö, S, Jacks, G. 2014. Recharge and sustainability of a coastal aquifer in Northern Albania. Hydrogeology Journal. 22, (4), 883–892.
Todd, D. K. 1959. Ground Water Hydrology, John Wiley and Sons. Inc, New York, 277–294.