用于衬垫生产的水处理污泥和软土混合物的力学和化学特性

L. Marchiori, André Studart, A. Albuquerque, L. Pais, M. Boscov, V. Cavaleiro
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引用次数: 1

摘要

粘土基和土工合成衬垫通常用作固体废物处理设施、采矿尾矿池和土壤基废水处理技术中的水力屏障,以避免有害化合物浸出到底土和地下水中。水处理污泥(WTS)是一种水处理厂(WTP)残渣,由于其水力特性似乎降低了WTS:土壤混合物的渗透性,可能成为生产可持续废物基衬垫的替代材料。本研究的目的是表征和分析WTS、软土和四种混合WTS:土按05:95%、10:90%、15:85%、20:80%的比例的物理、化学和力学参数。因此,评估生产用于土木工程应用的废物基衬垫的最佳比例。岩土力学表征:粒度分布、比表面积、比重、阿特伯格极限和普氏压实;通过x射线荧光(XRF)分析氧化物的化学成分,通过x射线衍射(XRD)和扫描电子显微镜(SEM)与能量色散光谱仪(EDS)耦合成像进行矿物学描述;力学性能表现为非计量固结、固结不排水(CU)三轴固结和下降水头渗透率。对所有混合物、土壤和WTS进行了测试,并指出了例外情况。结果表明,细粒WTS填充了土壤空隙,但重新排列了土壤颗粒,因此随着WTS的加入,压实干单位重降低,这可能与WTS的化学成分中含有大量的铝和硅有关。与土相比,压实混合物的可压缩性没有显著差异,而抗剪强度分析表明,WTS的加入降低了黏聚力,增加了有效内摩擦角。导电性随着WTS的增加而增加,直到10%的渣油引入,下降15%,继续下降20%,在15%达到最佳渗透率。WTS的掺入可以改善或不干扰土壤的性质,用作固体废物储存设施、采矿池塘和基于土壤的废水处理技术的衬垫材料。此外,15% WTS(15:85%混合物)掺入的效果最好,可以满足衬垫材料的水力传导性要求,即等于或低于10- 9m /s。在循环经济的范围内,WTS的再利用将允许生产一种新的增值材料。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Mechanical and Chemical Behaviour of Water Treatment Sludge and Soft Soil Mixtures for Liner Production
Clay-basedand geosynthetic liners are generally used as hydraulic barrier in solid waste disposal facilities, mining tailing ponds, and soil-based wastewater treatment technologies, avoiding leaching of hazardous compounds to subsoil and groundwater. Water treatment sludge (WTS) is a water treatment plant (WTP) residue which due to hydraulic properties seems to decrease the permeability in WTS:soil mixtures and may become an alternative material to produce sustainable waste-based liners. This research aims to characterize and analyse physical, chemical and mechanical parameters of a WTS, a soft soil and four mixtures WTS: soil following 05:95%, 10:90%, 15:85%, 20:80% ratios. Therefore, evaluate the best ratio for producing waste-based liners for civil engineering applications. The geotechnical characterization performing –particle size distribution, specific surface, specific gravity, Atterberg limits, and Normal Proctor compaction; chemical composition due to oxides analyses through X-ray fluorescence (XRF), mineralogical description by X-ray diffraction (XRD) and scanning electron microscope (SEM) with energy dispersive spectrometer (EDS) coupled for imaging; and mechanical behavior performing - –oedometric consolidation, consolidated undrained (CU) triaxial, and falling head permeability. Tests were conducted for all mixtures, the soil, and WTS, with pointed out exceptions. The results showed that the fine-grained WTS filled the soil voids but rearranging soil particles, thus, compacted dry unit weight decreased with WTS addition, probably due to its chemical composition with high amounts of aluminium and silica. The compressibility of the compacted mixtures did not differ significantly compared to the soil, while the shear strength analysis demonstrated a reduction in cohesion, and an increase in the effective internal friction angle proportional to WTS addition. Hydraulic conductivity increased with WTS until 10% of residue introduction, decreased for 15%, and continued to decrease for 20%, reaching optimum permeability in 15%. The incorporation of WTS can improve or just do not interfere at soil’s properties to be used as liner material in solid wastes storage facilities, mining ponds and soil-based wastewater treatment technologies. Furthermore, 15% of WTS (15:85% mixture) incorporation provided the best results meeting the hydraulic conductivity requirement for liner materials, i.e., equal, or lower than 10-9 m/s. The reuse of WTS for this purpose would allow producing a new added-value material in the scope of circular economy.
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