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LEACHATE MANAGEMENT OF PORT HOPE LONG-TERM WASTE MANAGEMENT FACILITY (LTWMF)

机译:港口希望长期废物管理设施(LTWMF)的渗滤液管理

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This paper explains the implementation and commissioning results for the leachate treatment system at the Port Hope Long Term Waste Management Facility (LTWMF). It will also summarize system performance to date. Approximately 1.2 million cubic meters of historic low-level radioactive waste (LLRW) resulting from historic uranium and radium processing operations located in various locations throughout urban Port Hope will be stored in this facility. Transfer of impacted waste to the facility began in 2018. A combination of precipitation, clarification, reverse osmosis (RO), and evaporation were selected for removal of radionuclides from LTWMF leachate as the most effective treatment method to achieve optimal contaminant removal. A schematic of the process is shown in Figure 1. Project commissioning was conducted in two separate phases. The first phase covered the commissioning and optimization of primary treatment and the RO system. The second phase included the commissioning and optimization of the residuals management system which included evaporative and slurry drying technologies. In the first phase, a polymer assisted clarification unit was implemented prior to the media filtration / RO treatment for removal of the suspended solids. In the residuals management phase, an evaporative system was used to further concentrate the RO concentrate stream into a highly concentrated brine. A slurry drying system was then used to dry the resulting brine to a solid suitable for disposal at the waste management facility. The paper will delve into the challenges faced during both phases of the commissioning process and explain how the leachate treatment system was adapted to meet these challenges. Challenges addressed will include the concentrating effects of concentrate recirculation on the primary collection lagoon and management of residuals water content. Phase 1 commissioning results showed that the Chemical of Concerns (COCs) concentrations met the design objectives. For instance, an average removal efficiency of 99.3 and 94.96 percent for total Uranium and Radium-226 were obtained, respectively. By considering the current discharge limits for uranium and radium-226 which are 0.15 mg/l and 0.37 Bq/l, respectively, it is predicted that this treatment system could handle the leachate with concentration of uranium dilution factor of 2.6 was estimated using a dispersion model for large lake coastal situations, and by assuming a 14 meters down shore distance mixing zone, the effluent concentration of these two radionuclides will fall below CCME short-term discharge limit for protection of freshwater aquatic life.
机译:本文解释了希望港长期废物管理设施(LTWMF)的沥滤液处理系统的实施和调试结果。还将总结迄今为止的系统性能。位于霍普港市区各处的历史铀和镭加工作业产生的约120万立方米历史低放射性废物(LLRW)将被存储在该设施中。从2018年开始将受影响的废物转移到工厂。选择了沉淀,澄清,反渗透(RO)和蒸发的组合以从LTWMF渗滤液中去除放射性核素,这是实现最佳污染物去除的最有效处理方法。图1中显示了该过程的示意图。项目调试是在两个单独的阶段中进行的。第一阶段涉及初级治疗和反渗透系统的调试和优化。第二阶段包括调试和优化残渣管理系统,其中包括蒸发和浆料干燥技术。在第一阶段中,在介质过滤/反渗透处理之前采用了聚合物辅助的澄清装置,以除去悬浮的固体。在残留物管理阶段,使用蒸发系统将反渗透浓缩液进一步浓缩成高浓度盐水。然后使用浆液干燥系统将所得盐水干燥成适合于在废物管理设施处处置的固体。本文将探讨调试过程中两个阶段所面临的挑战,并说明如何调整渗滤液处理系统以应对这些挑战。解决的挑战将包括浓缩液再循环对主要集水泻湖的​​浓缩作用和残留水含量的管理。第1阶段的调试结果表明,关注化学(COC)浓度符合设计目标。例如,总铀和镭226的平均去除效率分别为99.3%和94.96%。通过考虑铀和镭226的当前排放极限,分别为0.15 mg / l和0.37 Bq / l,可以预测该处理系统可以处理铀浓度为2.6的铀稀释系数的浸出液。该模型适用于大湖沿岸情况,并假设在距岸14米的混合区域内,这两种放射性核素的流出物浓度将降至CCME短期排放限值以下,以保护淡水水生生物。

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