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Leaching of elements from cement activated fly ash and slag amended soils

机译:水泥活化粉煤灰和矿渣改良土壤中元素的浸出

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Very few studies have investigated the leaching characteristics of cement activated fly ash and slag treated soils, although the inclusion of cement significantly enhances the material pH and may alter the leachability of elements. In this study the leaching behavior and mechanisms of chromium (Cr), copper (Cu), iron (Fe) and sulfur (S) from cement activated fly ash and slag stabilized soils were evaluated. An array of synthetic precipitation leaching procedure (SPLP), batch water leach test (WLT), toxicity characteristic leaching procedure (TCLP) and pH-Static leach tests were conducted. A geochemical equilibrium model Visual MINTEQ was implemented to identify the leaching controlling mechanisms of the metals. Results indicated that, the leached concentrations of Cr, Cu, Fe and S in SPLP, WLT and TCLP effluents were in the range of 0.016-0.74 mg/L, 0.013-0.17 mg/L, 0.019-0.27 mg/L and 1.78-234 mg/L, respectively. Quantitative comparisons between the standard test procedures suggested the necessity of multiple test methods for a comprehensive leaching assessment. Cr and Cu showed amphoteric leaching behaviors, whereas Fe and S followed cationic leaching patterns. According to the geochemical analyses, amorphous Cr(OH)(3); tenorite and Cu(OH)(2); ferrihydrite and goethite; gypsum and anhydrite; could control the leaching of Cr, Cu, Fe and S, respectively. The effluent Cr concentrations frequently exceeding the U.S. EPA specified maximum contaminant level of 0.1 mg/L Yet, the use of cement activated fly ash and slag mixed soils could be beneficial, since less toxic trivalent Cr (III) was identified through geochemical modeling. (C) 2019 Elsevier Ltd. All rights reserved.
机译:很少有研究调查水泥活化的粉煤灰和矿渣处理过的土壤的浸出特性,尽管水泥的掺入会显着提高材料的pH值并可能改变元素的浸出性。本研究评估了水泥活化粉煤灰和矿渣稳定土中铬(Cr),铜(Cu),铁(Fe)和硫(S)的浸出行为及其机理。进行了一系列合成沉淀浸出程序(SPLP),分批水浸出测试(WLT),毒性特征浸出程序(TCLP)和pH静态浸出测试。利用地球化学平衡模型Visual MINTEQ来识别金属的浸出控制机理。结果表明,SPLP,WLT和TCLP废水中Cr,Cu,Fe和S的浸出浓度分别为0.016-0.74 mg / L,0.013-0.17 mg / L,0.019-0.27 mg / L和1.78-0.7。分别为234 mg / L。标准测试程序之间的定量比较表明,必须采用多种测试方法进行全面浸出评估。 Cr和Cu表现出两性浸出行为,而Fe和S遵循阳离子浸出模式。根据地球化学分析,无定形Cr(OH)(3);钙长石和Cu(OH)(2);水铁矿和针铁矿;石膏和硬石膏可以分别控制Cr,Cu,Fe和S的浸出。废水中的Cr浓度经常超过美国EPA规定的最大污染物水平0.1 mg / L。然而,使用水泥活化的粉煤灰和矿渣混合土壤可能是有益的,因为通过地球化学模型确定了毒性较低的三价Cr(III)。 (C)2019 Elsevier Ltd.保留所有权利。

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