Evaluation of dike-type causeway impacts on the ow and salinity regimes in Urmia Lake, Iran Mostafa Zeinoddini a , Mohammad Ali Toghi b, , Fereydun Vafaee a,c a K.N.T.University of Technology, Iran, Faculty of Civil Eng.KNToosi University of Technology (KNTU),ValiAsr-Mirdamad Cross, Tehran,19697, Iran b Sharif University of Technology, Iran, Faculty of Civil Eng. Sharif University of Technology (SUT), Azadi Av, Tehran, Iran c Soil Conservation and Watershed Management Research Institute (SCWMRI), Iran, Coastal Department, (SCWMRI), P.O.Box 13445-1136, Tehran, Iran abstract article info Article history: Received 11 August 2007 Accepted 5 August 2008 Communicated by Dr. Ram Yerubandi Index words: Urmia Lake Hydrodynamic Advection-dispersion Salinity MIKE software Urmia Lake, located in a closed basin in north-west Iran, is the largest lake (50006000 km 2 ) in the Middle East. It is very saline with total dissolved salts reaching 200 g/l compared with a normal seawater salinity of about 35 g/l. The construction of a causeway, which was initiated in 1979 but then abandoned until the early 2000s, is near completion and will provide road access between the western and eastern provinces. The causeway has an opening 1.25 km long and divides Urmia Lake into a northern and southern basin and restricts water exchange. The ow and salinity regimes are affected by the presence of this new causeway, and there are concerns over the well being of the Artemia population. This study investigates the effects of the construction of the causeway on ow and salinity regimes, considers remedial actions, and examines the effects of climatic variability on salinity and ow. Flow and salinity regimes were numerically simulated by using a commercially available two and three-dimensional (2D and 3D) MIKE model. The validity of the numerical model was assessed through sensitivity analysis of the model and comparing the simulated results against eld measurements; the 3D model provided the higher correlation between simulated and actual data. Wind input was the main climatic and hydrologic factor inuencing ow regime while river discharge, evaporation and rainfall were the key parameters affecting salinity distribution in the lake models. The 3D model was subsequently used to predict lake conditions in typical dry, wet and normal climates, to examine the environmental impacts from the new causeway, and to evaluate possible improvements that some remedial measures may provide. © 2009 Elsevier Inc. All rights reserved. Introduction Urmia Lake is one of the largest salt lakes in the world and is located in a closed basin in north-west Iran (37 °4′–38 °17N and 45 ° 46 °E). The lake has a semi-rectangular shape, a maximum length of 135 km, and a surface area between 5000 and 6000 km 2 (Shabestari, 2003). A general map of Urmia Lake is presented in Fig. 1 and shows its bathymetry (Sadra, 2003) based on a water datum of 1275 m above the Persian Gulf Mean Sea Level (MSL). The mean water level varies seasonally (yearly) by about 1 m, with greater variations in water level occurring over longer time spans. For the 19302007 period, the extreme low of 1273.5 m occurred in 2002 and the extreme high of 1278.4 m in 1994. From 1979 to 1992, a 15.4 km dike-typecauseway was gradually constructed to cross the lake width at its narrowest part (Fig. 1) and to provide road access between the western and eastern provinces. This rubble mound embankment was built by direct dumping of the quarry run materials, concurrently, from the eastern and western shores with a 1.25 km long opening left in the causeway to provide for connection between the northern and southern parts of the lake. In the early 2000s, construction was accelerated to build a bridge to span this opening and thus complete the causeway. Thus this eastwest running dike-type causeway essentially divides the lake into northern and southern parts with a single opening allowing limited water ow between the two basins. Several rivers ow into Urmia Lake (Fig. 1) and, with an average annual inow of about 4.6 billion m 3 , are the main source of water to the lake. Some rivers ow over saline soils, picking up dissolved salts which are discharged with their ow into the lake; salinity is 6 g/l around some river mouths. Evaporation rates are high averaging 1200 mm/year for a 50 year record. As a result, the lake is highly saline with salinity averaging 225 g/l but may reach 280 g/l when the lake water level declines during dry years. Salinity is approximately 60% higher in the northern basin of the lake because of higher evaporation rates and lower water river inows than in the southern basin. Salinity and lake level have declined over the past 20 years although salinity did increase over 20032004 with favorable climatic conditions (Eimanifar and Mohebbi, 2007). Construction of the causeway may also have contributed to a higher salinity in the north and lower salinity in the south by reducing the normal exchange of water between the northern and southern parts of the lake. Journal of Great Lakes Research 35 (2009) 1322 Corresponding author. E-mail addresses: Zeinoddini@kntu.ac.ir (M. Zeinoddini), Toghi@civil.sharif.edu (M.A. Toghi), fvafai@kntu.ac.ir (F. Vafaee). 0380-1330/$ see front matter © 2009 Elsevier Inc. All rights reserved. doi:10.1016/j.jglr.2008.08.001 Contents lists available at ScienceDirect Journal of Great Lakes Research journal homepage: www.elsevier.com/locate/jglr