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Landfill modelling in LCA - A contribution based on empirical data

机译:LCA中的垃圾填埋场建模-基于经验数据的贡献

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Landfills at various stages of development, depending on their age and location, can be found throughout Europe. The type of facilities goes from uncontrolled dumpsites to highly engineered facilities with leachate and gas management. In addition, some landfills are designed to receive untreated waste, while others can receive incineration residues (MSWI) or residues after mechanical biological treatment (MBT). Dimension, type and duration of the emissions from landfills depend on the quality of the disposed waste, the technical design, and the location of the landfill. Environmental impacts are produced by the leachate (heavy metals, organic loading), emissions into the air (CH_4, hydrocarbons, halogenated hydrocarbons) and from the energy or fuel requirements for the operation of the landfill (SO_2 and NO_x from the production of electricity from fossil fuels). To include landfilling in an life-cycle assessment (LCA) approach entails several methodological questions (multi-input process, site-specific influence, time dependency). Additionally, no experiences are available with regard to mid-term behaviour (decades) for the relatively new types of landfill (MBT landfill, landfill for residues from MSWI). The present paper focuses on two main issues concerning modelling of landfills in LCA: Firstly, it is an acknowledged fact that emissions from landfills may prevail for a very long time, often thousands of years or longer. The choice of time frame in the LCA of landfilling may therefore clearly affect the results. Secondly, the reliability of results obtained through a life-cycle assessment depends on the availability and quality of Life Cycle Inventory (LCI) data. Therefore the choice of the general approach, using multi-input inventory tool versus empirical results, may also influence the results. In this paper the different approaches concerning time horizon and LCI will be introduced and discussed. In the application of empirical results, the presence of data gaps may limit the inclusion of several impact categories and therefore affect the results obtained by the study. For this reason, every effort has been made to provide high-quality empirical LCI data for landfills in Central Europe.
机译:在整个欧洲,都可以找到处于发展各个阶段的垃圾填埋场,具体取决于垃圾填埋场的年龄和位置。设施的类型从不受控制的垃圾场到具有渗滤液和气体管理的高度设计的设施。此外,有些垃圾填埋场设计为接收未经处理的废物,而其他垃圾填埋场则可以接收焚化残留物(MSWI)或机械生物处理后的残留物(MBT)。垃圾填埋场排放的尺寸,类型和持续时间取决于所处置垃圾的质量,技术设计以及垃圾填埋场的位置。环境影响是由渗滤液(重金属,有机物),向大气中的排放(CH_4,碳氢化合物,卤代碳氢化合物)以及垃圾填埋场运行所需的能量或燃料(SO_2和NO_x)所产生的。化石燃料)。将垃圾填埋场纳入生命周期评估(LCA)方法涉及几个方法学问题(多输入过程,特定地点的影响,时间依赖性)。此外,对于相对较新类型的垃圾填埋场(MBT垃圾填埋场,MSWI残留物垃圾填埋场),没有关于中期行为(十年)的经验。本文着重讨论了有关LCA中垃圾填埋场建模的两个主要问题:首先,一个公认的事实是,垃圾填埋场的排放可能会持续很长时间,通常是数千年甚至更长。因此,在LCA填埋场中选择时间范围可能会明显影响结果。其次,通过生命周期评估获得的结果的可靠性取决于生命周期清单(LCI)数据的可用性和质量。因此,使用多输入清单工具而不是经验结果来选择一般方法也可能会影响结果。在本文中,将介绍和讨论有关时间范围和LCI的不同方法。在实证结果的应用中,数据缺口的存在可能会限制包括几个影响类别,因此会影响研究获得的结果。因此,我们已尽一切努力为中欧的垃圾填埋场提供高质量的LCI经验数据。

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