Laserfiche WebLink
• • Cases and solutions <br />~m <br />m <br />'- c <br />~ u <br />`m <br />ca <br />fig. 6 <br />Sie~•~ ~.tnalysis of unconsolidated soils <br />Table 2 <br />Basic characteristics of unconsolidated soils in the study area <br />Ground surface and Wit <br />m <br />0 <br />P2 <br />Pt <br />5 <br />®P2-Pt <br />(not scale) <br />Fig. 7 <br />The unconsolidated soil and travertine profile <br />with hydrological conditions and pumping. It was ob- <br />served that water level in the lake reached the E]ooding <br />point in the period of April-M1lah 1996. Based on the data <br />from Meteorology Station of Ni~de, annual average rain- <br />fall is 341.76 mm between the years 19i1-199]. <br />basic characteristics average <br />resuhs <br />specific gravity (Gs) 2.61 <br />water content (w), % 34 <br />unit weight (y„), kN/m~ 12.85 <br />saturated unit weight (y,), kN/ms 14.71 <br />physical properties of unconsolidated soils are given in <br />Table 2. <br />Typical unit weights in clay range from 1.5 to 2.0 Ivig/m', <br />'while they vary between 1.4 and 2.0 Mg/ma in sand (At- <br />tawell and Farmer 1976). Average unit weight value in <br />'the unconsolidated soils around the Lake Dipsiz is found <br />ito be too low (12.85 kN/ms=1.31 Mg/ma). If the Ter- <br />Izaghi equation (1943) is applied to the region, each 1-m <br />Sdro; of groundwater level in unconsolidated soils will <br />kwuse a 7.947 kN/m~ increase in the effective stress above <br />Rthe [ravertines (Table 3, Fig. 7). <br />iroundwater Elow direction of unconfined aquifer is in a <br />iWNW direction in the study area (Giilenbay 1972). <br />(Hence, we believe that waters oEChe Akkaya Dam could <br />;not be affected from the solution-subsidence develop- <br />ment. Topographic elevation of Lake Dipsiz is 1201 m <br />Viand its water level is 1197 m. Groundwater level changes <br />Karstic occurences in Lake Dipsiz <br />and adjoining areas <br />Karstic travertine with cavern porosity underlies the un- <br />consolidated clayey and silty sand soils in the Lake Dip- <br />siz and its surroundings. There exist organic soils and <br />carbonated strata that have a thickness of about 5 cm in <br />Lake Dipsiz and surroundings. <br />It is assumed that Lake Dipsiz has been cohered by un- <br />consolidated soils in the geological age. Groundwater lev- <br />el has fluctuated due to aquifer recharges and discharges, <br />dominated by runoff and groundwater in the study area. <br />It was formed b)• the subsidence of unconsolidated soils <br />as landslide into a karstic cave (Fig. 3). <br />Excessive dratvdown has occurred as a result of excessive <br />pumping (23 September 1995: 300 I/s) in Lake Dipsiz due <br />[o the effect of human needs on groundwater. Excessive <br />pumping has been cu[ down on the required groundwa- <br />ter period (at least 3 months per year). Unconsolidated <br />soils subsiding vertically to the voids of capes during the <br />water table fluctuation resulted in solution subsidence. It <br />is generally accepted that sinkholes induced by human <br />Table 3 <br />anon of effective stress due to groundwater depth (1=groundwater level at ground surface, I1=groundwater level 5 m deep <br />travertine depth assumed 5 m below the ground surface) <br />unconsolidated P, P„ P=(P,-PH) result <br />soil kN/m' kN/m' kN/m' kN!m' <br />thickness, m <br />5x14.71=73.55 5X9.807=49.035 73.55-49.035=24.515 Il-1= <br />5X12.85=6-1.25 0 6-1._'5-0=64.25 39.; i5~.5=7.9x7 <br />Environmental Geology 36 13-4) Decemi!er 1998 ~ '- Springer-Verlag 1339 - <br />Particle size (mm) <br />