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Compressibility Parameters of Municipal Solid Waste with Leachate Recirculation

机译:城市固体废物的可压缩性参数渗滤液再循环

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The operation of landfills with leachate recycle (bioreactors) enhances refuse decomposition and offers a number of advantages including leachate treatment and disposal as well as recovery and reuse of landfill airspace. However, settlement models have not been applied and tested in these situations. Work in this paper utilize measured data from leachate recycle test cell A, at the Mountain View controlled landfill Project, and results from laboratory oedometer testing to illustrate the feasibility of predicting waste compressibility in bioreactor landfills. The merits of the proposed method are the identification of the degradation phase, and the application of the proper compressibility parameters corresponding to the dominating mechanics of settlement (mechanistic, creep, or biological). Measured parameters from the laboratory tests on samples at Phase 1 stage of decomposition indicated creep index (C_(α1)) of 0.03 and biological degradation index (C_β1)) of 0.05. This value is approximately the sameC_(α2) of 0.03 for Phase 2 sample. As decomposition is accelerated over a period of 13 days, the sample degraded into Phase 3 and C_(β3) was estimated to be 0.19. Using these parameters and onset time of accelerated gas production to be 500 days, the measured settlement strain in the field is closely estimated. Beyond applicability of the method illustrated here to field test data, challenges arise in application to prototype landfills. These include the definition of compressibility properties of each waste sub-layer as a function of decomposition stage and moisture content as time progresses throughout the operation and post closure periods and until waste stability is reached.
机译:垃圾填埋场与浸出液回收(生物反应器)的操作增强了垃圾分解,提供了许多优点,包括渗滤液处理和处理以及垃圾填埋空间的恢复和重用。但是,在这些情况下尚未应用和解解决模型。本文的工作利用来自湖景控制垃圾填埋场的渗滤液再循环试验单元A的测量数据,并由实验室测量计测试结果来说明预测生物反应器垃圾填埋场中的废物压缩性的可行性。所提出的方法的优点是识别降解阶段,以及适用于定位的主导机制(机械,蠕变或生物)的主要压缩参数。来自实验室测试的测量参数在分解的第1阶段的样品上的试验表明蠕变指数(C_(α1))0.03和生物降解指数(C_β1))为0.05。该值大约是相2样品0.03的Samec_(α2)。由于分解在13天的时间内加速,将样品降解成相3和C_(β3),估计为0.19。使用这些参数并开始加速气体产生的时间为500天,估计该领域的测量沉降应变。除了这里所示的方法的适用性超越现场测试数据,挑战在应用于原型垃圾填埋场。这些包括作为分解阶段和水分含量的函数的每个废物子层的可压缩性质的定义,因为时间在整个操作和后闭合时期进行,直到达到废物稳定性。

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