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Interface transmissivity and hydraulic conductivity of GCLs below poured concrete

机译:浇筑混凝土下面的GCL的界面透射率和水导率

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The performance of four geosynthetic clay liners (GCLs) used as a hydraulic barrier below concrete-lined sewage treatment lagoons was examined based on a series of laboratory tests aimed at measuring: (i) the lateral flow of synthetic wastewater through the interface between each GCL product and a 0.1 m thick cast-in-place concrete above the GCL over a 14-month period and, from this data, calculating the concrete/GCL interface transmissivity (theta); and (ii) the hydraulic conductivity (k) of the GCLs below poured concrete when exposed to (iia) synthetic wastewater under isothermal conditions, or (iib) a series of wet-dry and/or cool-heat cycles for up to 12 months. The four GCLs have either sodium or polymer-enhanced sodium bentonite, and either granular or powdered bentonite. When the wastewater head above the GCL was 1.0 m (stress on concrete, sigma = 10 kPa), L for the GCL with granular sodium bentonite was 4 X 10(-11) m(2)/s. For the same GCL, when the head increased to 2.5 m (sigma = 25 kPa), the value of L was reduced by about one order of magnitude to 2 X 10(-12) m(2)/s. For the GCL which has polymer-enhanced granular bentonite, the value of L was similar to (and possibly lower than) that for the GCL with untreated granular bentonite. For the GCL with powdered bentonite and cover geotextile impregnated with 1280 g/m(2) of bentonite, the values of L were 2 X 10(-12) and 4 X 10(-13) m(2)/s at 1.0 and 2.5 m head, respectively. With a reduction in the amount of the impregnated powdered bentonite in the cover geotextile to 840 g/m(2), theta was 1 to 9 X 10(-12) m(2)/s. The lowest k (3.2 X 10(-11) m/s) for a GCL below concrete and exposed to wastewater under isothermal conditions was measured for the GCL with polymer-enhanced granular bentonite, whereas the highest value of k (1.9 X 10(-10) m/s) was for the GCL with standard granular bentonite. Under 0.5 m head and 3 kPa stress, the k of the GCL below concrete and exposed to wet-dry cycles was 1.2-2.6 times the k of the GCL exposed to wastewater under isothermal conditions. Analytical calculations for the leakage through concrete/GCL liners for the four GCLs showed that the leakage was below the allowable limits specified by the Australian, British, and American standards.
机译:根据一系列旨在测量以下内容的实验室测试,检查了四个衬砌的水泥衬里(GCL)在混凝土衬砌的污水处理泻湖下作为水力屏障的性能:(i)通过每个GCL之间的界面的合成废水的侧向流动产品和GCL上方的0.1 m厚现浇混凝土,历时14个月,并根据此数据计算混凝土/ GCL界面的透射率(θ); (ii)在等温条件下暴露于(iia)合成废水中时,或(iib)一系列长达12个月的干湿和/或冷热循环时,浇筑混凝土下方的GCL的水力传导率(k) 。四个GCL含有钠或聚合物增强的钠膨润土,以及粒状或粉状膨润土。当GCL上方的废水扬程为1.0 m(混凝土上的应力,sigma = 10 kPa)时,含钠膨润土颗粒的GCL的L为4 X 10(-11)m(2)/ s。对于相同的GCL,当压头增加到2.5 m(sigma = 25 kPa)时,L值减小了大约一个数量级,为2 X 10(-12)m(2)/ s。对于具有聚合物增强的粒状膨润土的GCL,L值类似于(可能低于)未经处理的粒状膨润土的GCL。对于含有膨润土粉和覆盖有1280 g / m(2)膨润土的土工布的GCL,在1.0和1.0的条件下,L的值为2 X 10(-12)和4 X 10(-13)m(2)/ s。分别为2.5 m头。随着覆盖土工布中浸渍的粉状膨润土数量减少到840 g / m(2),θ为1到9 X 10(-12)m(2)/ s。对于使用聚合物增强粒状膨润土的GCL,在混凝土下面并在等温条件下暴露于废水中的GCL的最低k(3.2 X 10(-11)m / s)进行了测量,而kCL的最大值(1.9 X 10( -10)m / s)用于具有标准粒状膨润土的GCL。在0.5 m水头和3 kPa应力下,混凝土下面并暴露于干湿循环的GCL的k是等温条件下暴露于废水的GCL的k-的1.2-2.6倍。对四个GCL的混凝土/ GCL衬里泄漏的分析计算表明,泄漏量低于澳大利亚,英国和美国标准规定的允许极限。

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