Abstract:A study was conducted to stabilize low stiffness road surface material with high carbon fly ash. The non-cementitious Maryland fly ash was activated with another recycled material, lime kiln dust (LKD). California bearing ratio (CBR) and resilient modulus tests were conducted to determine the strength and stiffness, respectively, of the stabilized materials. Addition of LKD and curing of specimens generally increased CBR and summary resilient modulus (SM R ) and lowered plastic strains, whereas fly ash additio… Show more
“…The reason for the increase in the optimum water content is an increase in the particle surface area of samples due to the addition of finer materials. Similar trends have been obtained from some experimental works [3,4,5,6,7].…”
Section: Resultssupporting
confidence: 89%
“…There are a lot of studies about fly ash used in the stabilization of soils. In the previous studies [2,3,4,5,6,7] it was indicated that the engineering properties of fly ash amended soils have been improved. Generally, fly ash was used together with different additive materials like cement, lime or industrial wastes like marble dust, cement kiln dust, etc.…”
“…The reason for the increase in the optimum water content is an increase in the particle surface area of samples due to the addition of finer materials. Similar trends have been obtained from some experimental works [3,4,5,6,7].…”
Section: Resultssupporting
confidence: 89%
“…There are a lot of studies about fly ash used in the stabilization of soils. In the previous studies [2,3,4,5,6,7] it was indicated that the engineering properties of fly ash amended soils have been improved. Generally, fly ash was used together with different additive materials like cement, lime or industrial wastes like marble dust, cement kiln dust, etc.…”
“…This reaction of fly ash with lime in concrete improves strength. Cetin et al [11] reported that the CBR value of the soil stabilized with fly ash (10% and 20%) and lime kiln dust (2.5% and 5%) were found to be In the same way, alternate layers of fly ash overburden admixture and overburden only was filled in the void. Thus, each layer of admixture of fly ash overburden was followed by a layer of overburden.…”
Section: Mechanism Of Stabilization Of Slope With Fly Ashmentioning
Fly ash is mainly being utilized for making cement, bricks, concrete, roads and small quantity in mine void filling. The consumption of fly ash in construction activity has reached to almost saturation level and there is not much potential to consume more fly ash in these segments. Mining sector like mine void filling, underground stowing and mixing with overburden of open cast mine are the only potential area where bulk quantity of fly ash can be utilized so that 100% utilization target can be achieved. There are more than 165 opencast coal mines in India and many are near to thermal power stations. Opencast mining plays a major role in meeting the demand of coal for thermal power generation. The stability of overburden dumps stands at high priority from the safety and economic perspective. This paper investigates the suitability of fly ash to be disposed of by mixing it with overburden (OB) dumps to increase the slope stability in coal mines. This paper attempts to highlight the utilization of fly ash for slope stabilization of overburden during backfilling, in order to save our environment. This paper presents various open cast coal mine where fly ash has been successfully disposed in overburden dump material.
“…The use of recycle materials in pavement systems in lieu of natural aggregates has been an interest for some time (Tanyu et al 2005;Li et al 2009;Cetin et al 2010). Crushed waste concrete, termed recycled concrete aggregate (RCA), is also considered as an alternative material to be used in roadway construction (Chen et al 2013).…”
Leaching of metals (calcium (Ca), chromium (Cr), copper, (Cu), iron (Fe), and zinc (Zn)) of recycled concrete aggregates (RCAs) were investigated with four different leachate extraction methods (batch water leach tests (WLTs), toxicity leaching procedure test (TCLP), synthetic precipitation leaching procedure test (SPLP), and pH-dependent leach tests). WLTs were also used to perform a parametric study to evaluate factors including (i) effects of reaction time, (ii) atmosphere, (iii) liquid-to-solid (L/S) ratio, and (iv) particle size of RCA. The results from WLTs showed that reaction time and exposure to atmosphere had impact on leaching behavior of metals. An increase in L/S ratio decreased the effluent pH and all metal concentrations. Particle size of the RCA had impact on some metals but not all. Comparison of the leached concentrations of metals from select RCA samples with WLT method to leached concentrations from TCLP and SPLP methods revealed significant differences. For the same RCA samples, the highest metal concentrations were obtained with TCLP method, followed by WLT and SPLP methods. However, in all tests, the concentrations of all four (Cr, Cu, Fe, and Zn) metals were below the regulatory limits determined by EPA MCLs in all tests with few exceptions. pH-dependent batch water leach tests revealed that leaching pattern for Ca is more cationic whereas for other metals showed more amphoteric. The results obtained from the pH-dependent tests were evaluated with geochemical modeling (MINTEQA2) to estimate the governing leaching mechanisms for different metals. The results indicated that the releases of the elements were solubility-controlled except Cr.
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