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Assessment of biogeochemical deposits in landfill leachate drainage systems: Phase II.

机译:垃圾渗滤液排水系统中生物地球化学沉积物的评估:第二阶段。

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Land disposal of solid waste is a vital component of any solid waste management system. Design, operation and closure of municipal solid waste (MSW) landfills are required by regulations to control leachate and gases generated during the life, closure, and post-closure of the facility. Clogging of leachate drainage and removal systems in landfills is a common phenomenon and has been acknowledged in several landfills throughout the United States and abroad.; This project was conducted in two phases. Phase I was completed in February of 2005 and Phase II was completed in August of 2006. Leachate characteristics data obtained in Phase I was processed and analyzed, along with supplementary data obtained in Phase II on liquid and solid phase testing. Leachate samples from the landfill and lysimeters indicated the presence of iron and sulfate-reducing bacteria. These bacteria are known to facilitate biologically induced precipitate formation.; The mechanism by which biologically induced precipitate may form begins with oxidizing acetate by iron and sulfate-reducing bacteria, reducing sulfate to sulfide and ferric iron to ferrous, and then forming calcium carbonate, iron sulfate, and possibly dolomite and other minerals.; The results show that the clogging mechanism is driven by two major processes: transformation of volatile acids to substrates by iron and sulfate-reducing bacteria causing local pH and total carbonate to increase, which accelerate calcium carbonate precipitation, and thermodynamically favored reactions in supersaturated conditions based on saturation indices of calcium, sulfide, iron, and other species with respect to minerals. For each 1 mg of consumed volatile acids there were 1.7 mg of calcium, 0.28 mg of sulfate, and 0.03 mg of iron removed.; Field and lysimeter precipitate samples were analyzed (using X-Ray Diffraction, Scanning Electron microscopy, and Electron Dispersive Spectroscopy) and correlated with geochemical modeling of leachate constituents. Precipitate analyses showed the presence of calcium carbonate, brushite (calcium phosphate), and dolomite, where as geochemical modeling showed that calcium carbonate, hydroxyapatite (complex of calcium phosphate), dolomite, pyrite, and siderite may be formed from field and lysimeter leachate constituents. The results also showed that submerged and stagnant conditions in the leachate collection systems accelerate the precipitation process.
机译:固体废物的土地处置是任何固体废物管理系统的重要组成部分。法规要求设计,操作和关闭城市固体废物(MSW)垃圾填埋场,以控制设施的寿命,关闭和关闭后的渗滤液和产生的气体。垃圾填埋场中沥滤液排泄和清除系统的堵塞是一种普遍现象,并且在美国和国外的一些垃圾填埋场中都得到了认可。该项目分两个阶段进行。第一阶段于2005年2月完成,第二阶段于2006年8月完成。处理和分析了第一阶段获得的渗滤液特征数据,以及第二阶段在液相和固相测试中获得的补充数据。来自垃圾填埋场和溶渗仪的渗滤液样品表明存在还原铁和硫酸盐的细菌。已知这些细菌可促进生物诱导的沉淀物形成。生物形成沉淀的机理始于还原铁和硫酸盐的细菌将乙酸盐氧化,将硫酸盐还原为硫化物,将三价铁还原为亚铁,然后形成碳酸钙,硫酸铁,并可能形成白云石和其他矿物。结果表明,堵塞机理是由两个主要过程驱动的:通过减少铁和硫酸盐的细菌将挥发性酸转化为底物,导致局部pH值和总碳酸盐增加,从而加速碳酸钙沉淀;以及在过饱和条件下热力学上有利的反应钙,硫化物,铁和其他物种相对于矿物质的饱和指数。每消耗1毫克挥发性酸,就会除去1.7毫克钙,0.28毫克硫酸盐和0.03毫克铁。分析了现场和溶渗仪沉淀物样品(使用X射线衍射,扫描电子显微镜和电子分散光谱),并与渗滤液成分的地球化学模型相关。沉淀分析表明存在碳酸钙,透钙磷石(磷酸钙)和白云石,而根据地球化学模型,碳酸钙,羟基磷灰石(磷酸钙的复合物),白云石,黄铁矿和菱铁矿可能由渗滤液和渗滤液渗出物成分形成。 。结果还表明,渗滤液收集系统中的淹没和停滞状态加速了沉淀过程。

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