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Hydraulic Conductivity of Environmentally Controlled Landfill Liner Test Pad

机译:环境控制垃圾填埋衬垫试验垫的液压导电性

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摘要

Laboratory and field hydraulic conductivity tests have been conducted on soil samples to develop and verify the zone of acceptance for liner placement. Compaction testing and flexible wall hydraulic conductivity tests were performed on fifteen (15) samples to determine the dry unit weight, molding water content, and laboratory permeability. Five of the fifteen samples were compacted at Standard proctor energy, five were compacted at 75 percent of Standard proctor energy, and five were compacted at 50 percent of Standard proctor energy. The results obtained from the laboratory portion of the testing program (the zone of acceptance) are presented. A ten foot-long by ten foot-foot wide by four foot tall box was created in an environmentally controlled environment (indoor lab). Six inches of sand were placed in the bottom of the box and overlain with a geotextile filter fabric. An eight-inch thick loose lift of clay was then placed, and compacted into a six-inch thick lift using two passes of a vibratory plate compactor. Five nuclear density tests were conducted on the first lift to ensure the soil was compacted within the zone of acceptance. This procedure was then continued for the remaining three lifts. A two-stage borehole (TSB) hydraulic conductivity test was conducted at the center of the test pad. The first stage (vertical) was conducted at 10 inches below the top of the liner, and the second stage (horizontal) was conducted from 10 inches to 16 inches below the top of the liner. The results obtained from the environmentally controlled TSB test were compared against tests conducted on landfill liner tests pads constructed at three different landfills within the state of Missouri. Two of the landfill liner tests pads were covered with tents while one was not covered. The results obtained from the environmentally controlled TSB did not display the same changes in hydraulic conductivity associated with diurnal cycles of direct sunlight that were observed in the landfill test pads. These diurnal cycles may result in a placement technique being rejected.
机译:实验室和现场导水试验已对土壤样品进行开发和验证验收区的衬垫置入。压实测试和柔性壁的水力传导率试验是在十五(15)的样品上进行,以确定干单位重量,成型的水含量,和实验室渗透性。在15个样本中有五个在标准监考能源压实,五在标准监考能源的75%都被压缩,而五人在标准监考能量的50%压缩。从测试程序(验收的区)的实验室部分所获得的结果。一个10英尺长,十英尺英尺宽四英尺高箱是在环境控制环境(室内实验室)创建的。沙六英寸放置在盒子的底部,并用土工布过滤布覆盖。然后粘土的八英寸厚松散升降机放置,并压制成使用振动板压实机的两次通过一个六英寸厚的升力。五个核密度测试在第一电梯进行,以确保土壤接受的区域内被压实。然后,这个过程持续其余三部电梯。两阶段钻孔(TSB)水力传导率测试在测试垫的中心进行的。第一阶段(垂直)的混合物在下面的衬管的顶部10英寸中进行,第二阶段(水平)从10英寸到下面的衬管的顶部16英寸进行。从环境控制测试TSB中获得的结果与在密苏里州内的三个不同的构建填埋垃圾填埋衬垫测试垫进行的测试进行比较。的垃圾填埋场衬垫测试垫两个布满了帐篷,而一个没有被覆盖。从环境控制的TSB中获得的结果没有显示在水力传导率产生的垃圾测试垫中观察到直射日光的昼夜交替相关联的相同的变化。这些昼夜交替可能导致被拒绝的放置技术。

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