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Site-specific aftercare completion criteria for sustainable landfilling in the Netherlands: Geochemical modelling and sensitivity analysis

机译:荷兰可持续填埋场针对特定地点的善后完成标准:地球化学建模和敏感性分析

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A novel, regulatory accepted approach is developed that enables competent authorities to decide whether landfill aftercare can be reduced or terminated. Our previous paper (Brand et al., Waste Management 2016, 56, 255–261,https://doi.org//10.1016/j.wasman.2016.07.038)outlines the general approach, that consists of a 10-year treatment phase (e.g., aeration, leachate recirculation), in combination with site-specific Environmental Protection Criteria (EPC) for contaminant concentrations in the landfill leachate after treatment. The current paper presents the unique modelling approach by which the site-specific EPC are derived. The modelling approach is based on the use of mechanistic multi-surface geochemical models covering the main sorption processes in soils underneath the landfills, and is composed of widely-accepted surface complexation models in combination with published “generic” parameter sets. This approach enables the consideration of the main site-specific soil properties that influence the attenuation of emitted contaminants. In addition, the sensitivity of the EPC is shown for variation of the main physicochemical-assumptions and policy-based decisions. Site-specific soil properties have been found to substantially determine the EPC and include soil-pH, dissolved organic matter, and iron-(hydr)oxide content. Apart from the sorption capacity of the local soil, EPC also depend strongly on the assumed dilution with local groundwater in the saturated zone. An important policy-related decision that influences the calculated EPC is the assessment period during which the groundwater is protected. The transparent setup of the approach using geochemical modelling, the explicit consideration of site-specific properties and the achieved regulatory acceptance may also stimulate application to landfills in other countries.
机译:开发了一种新颖的,法规接受的方法,使主管部门可以决定是否可以减少或终止垃圾掩埋的善后工作。我们之前的论文(Brand等人,Waste Management 2016,56,255-261,https://doi.org//1​​0.1016/j.wasman.2016.07.038)概述了一般方法,该方法由10年组成处理阶段(例如,曝气,渗滤液再循环),结合针对处理后垃圾填埋场渗滤液中污染物浓度的特定场所环境保护标准(EPC)。本文介绍了独特的建模方法,通过该方法可以导出特定于站点的EPC。该建模方法基于机械化多表面地球化学模型的使用,该模型涵盖了垃圾填埋场下方土壤中的主要吸附过程,并且由广泛接受的表面络合模型与已发布的“通用”参数集组成。这种方法可以考虑影响排放污染物衰减的特定地点的主要土壤特性。此外,还显示了EPC对主要理化假设和基于政策的决策的变化的敏感性。已发现特定地点的土壤特性可实质确定EPC,包括土壤的pH值,溶解的有机物和氧化铁(氢)含量。除当地土壤的吸附能力外,EPC还强烈取决于假定在饱和区中用当地地下水进行的稀释。影响计算得出的EPC的一项重要的与政策相关的决定是评估地下水的保护期。使用地球化学建模方法的透明设置,对特定地点属性的明确考虑以及已获得的法规认可也可能会刺激在其他国家/地区中对填埋场的应用。

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