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Mass balance evaluation of polybrominated diphenyl ethers in landfill leachate and potential for transfer from e-waste

机译:垃圾渗滤液中多溴二苯醚的质量平衡评估以及从电子废物转移的可能性

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Previous research on brominated flame retardants (BFRs), including polybrominated diphenyl ethers (PBDEs) has largely focussed on their concentrations in the environment and their adverse effects on human health. This paper explores their transfer from waste streams to water and soil. A comprehensive mass balance model is developed to track polybrominated diphenyl ethers (PBDEs), originating from e-waste and non-e-waste solids leaching from a landfill. Stepwise debromination is assumed to occur in three sub-systems (e-waste, aqueous leachate phase, and non-e-waste solids). Analysis of landfill samples and laboratory results from a solid-liquid contacting chamber are used to estimate model parameters to simulate an urban landfill system, for past and future scenarios. Sensitivity tests to key model parameters were conducted. Lower BDEs require more time to disappear than high-molecular weight PBDEs, since debromination takes place in a stepwise manner, according to the simplified reaction scheme. Interphase mass transfer causes the decay pattern to be similar in all three sub-systems. The aqueous phase is predicted to be the first sub-system to eliminate PBDEs if their input to the landfill were to be stopped. The non-e-waste solids would be next, followed by the e-waste sub-system. The model shows that mass transfer is not rate-limiting, but the evolution over time depends on the kinetic degradation parameters. Experimental scatter makes model testing difficult. Nevertheless, the model provides qualitative understanding of the influence of key variables.
机译:先前对包括多溴二苯醚(PBDEs)在内的溴化阻燃剂(BFR)的研究主要集中在其在环境中的浓度及其对人体健康的不利影响。本文探讨了它们从废物流向水和土壤的转移。建立了一个全面的质量平衡模型来跟踪多溴联苯醚(PBDEs),其源自垃圾填埋场中的电子垃圾和非电子垃圾固体。假定逐步脱溴发生在三个子系统(电子废物,浸出水相和非电子废物固体)中。固液接触室的垃圾填埋场样品分析和实验室结果用于估计模型参数,以模拟过去和将来的情景中的城市垃圾掩埋系统。对关键模型参数进行了敏感性测试。与低分子量的PBDEs相比,较低的BDEs需要更多的时间才能消失,这是因为根据简化的反应方案,脱溴作用是逐步进行的。相间质量传递导致所有三个子系统的衰减模式相似。如果要停止向垃圾填埋场输入多溴二苯醚,则预计水相将是消除多溴二苯醚的第一个子系统。接下来是非电子废物固体,其次是电子废物子系统。该模型表明传质没有速率限制,但随时间的演变取决于动力学降解参数。实验性分散使模型测试变得困难。但是,该模型可以对关键变量的影响进行定性理解。

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