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城市生活垃圾填埋场沉降监测与分析
引用本文:徐晓兵,詹良通,陈云敏,魏海云,林伟岸.城市生活垃圾填埋场沉降监测与分析[J].岩土力学,2011,32(12):3721-3727.
作者姓名:徐晓兵  詹良通  陈云敏  魏海云  林伟岸
作者单位:1.浙江大学 软弱土与环境土工教育部重点实验室,杭州 310058;2.天华建筑设计有限公司,上海 200233;3.浙江省水利河口研究院,杭州 310020
基金项目:国家自然科学基金项目,中央高校基本科研业务费专项资金资助,苏州市科技支撑计划项目
摘    要:2006年9月起于上海老港填埋场开展了示范工程沉降监测项目。该生活垃圾填埋场占地面积约为200 m×125 m,共填埋了约15×104 t来自上海城区的生活垃圾,最大填埋厚度约为9 m。通过填埋期间埋设的水平沉降管,监测到该填埋场不同埋深处的沉降值。介绍了沉降监测系统的工作原理,分析了2006年底至2008年底为期两年的沉降数据。填埋场底部沉降管监测数据表明,场底地基沉降较小,两年的平均沉降为 ~ cm;中部沉降管监测数据表明,该沉降管下方生活垃圾在上方垃圾填埋后产生了较大的压缩,从上方垃圾开始填埋至填埋完毕3个月内的压缩应变约为0.197~0.242;顶部沉降管和中部沉降管监测数据表明,该填埋场垃圾主压缩完成时间约为3个月;由于填埋垃圾有机物含量较高,其修正次压缩指数较大,约为0.066~0.070。

关 键 词:城市生活垃圾  沉降  主压缩  次压缩  
收稿时间:2010-05-18

Field monitoring and analysis of municipal solid waste landfill settlement
XU Xiao-bing,ZHAN Liang-tong,CHEN Yun-min,WEI Hai-yun,LIN Wei-an.Field monitoring and analysis of municipal solid waste landfill settlement[J].Rock and Soil Mechanics,2011,32(12):3721-3727.
Authors:XU Xiao-bing  ZHAN Liang-tong  CHEN Yun-min  WEI Hai-yun  LIN Wei-an
Institution:1. Key Laboratory of Soft Soils and Geoenvironmental Engineering, Ministry of Education, Zhejiang University, Hangzhou 310058, China; 2. Tianhua Architecture Planning Engineering Limited, Shanghai 200233, China; 3. Zhejiang Institute of Hydraulics and Estuary, Hangzhou 310020, China
Abstract:Settlement monitoring of a field-scale municipal solid waste landfill site in Shanghai Laogang Landfill was conducted since September 2006. The landfill site covered an area of 200 m×125 m and accepted about 150 000 tones of municipal solid waste from Shanghai. Maximum height of the wastes is about 9 m. Settlements at different depths of the landfill site during filling and after closure were monitored through horizontal inclinometers. The working principle of the horizontal inclinometer was introduced. Two years’ monitoring data showed that bottom horizontal inclinometers settled from -3.6 cm to -5.7 cm. Wastes under the middle horizontal inclinometers experienced large compression due to the deposition of overlying wastes. The compression strain from the beginning of the overlying wastes’ deposition to three months after the end of the deposition was about 0.197-0.242. Monitoring data from the top and middle horizontal inclinometers indicated that the time needed for the primary compression of wastes in the test site was about 3 months. Modified secondary compression index C’α was about 0.066-0.070, and was relatively large compared to published data which might due to the large amount of organic matter in the landfilled wastes.
Keywords:municipal solid waste  settlement  primary compression  secondary compression  
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