首页> 外文期刊>The Science of the Total Environment >CO_2 and N_2O from water resource recovery facilities: Evaluation of emissions from biological treatment, settling, disinfection, and receiving water body
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CO_2 and N_2O from water resource recovery facilities: Evaluation of emissions from biological treatment, settling, disinfection, and receiving water body

机译:水资源回收设施中的CO_2和N_2O:评估生物处理,沉降,消毒和接收水体的排放

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Water resource recovery facilities (WRRFs) contribute to climate change and air pollution, as they are anthropogenic potential sources of direct and indirect emission of greenhouse gases (GHGs). Studies concerning the monitoring and accounting for GHG emissions from WRRFs are of increasing interest. In this study, the floating hood technique for gas collection was coupled with the off-gas method to monitor and apportion nitrous oxide (N2O) and carbon dioxide (CO2) emissions from both aerated and non-aerated tanks in a municipal water resource recovery facility, in order to investigate its carbon footprint (CFP). To our knowledge, this is the first time that the chamber technique was applied to evaluate gas fluxes from the settler, where an emission factor (EF) of 4.71 *10(-5) kg(CO2,eq) kg(bCOD)(-1) was found. Interesting results were found in the disinfection unit, which was the major contributor to direct N2O emissions (with a specific emission factor of 0.008 kg(CO2,eq) kg(bCOD)(-1)), due to the chemical interaction between hydroxylamine and the disinfectant agent (hypochlorite). The specific emission factor of the biological aerated tank was 0.00112 kg(CO2,eq) kg(bCOD)(-1). The average direct CO2 emission was equal to 0.068 kg(CO2) kg(bCOD)(-1) from the activated sludge tank and to 0.00017 kg(CO2) kg(bCOD)(-1) from the secondary clarifier. Therefore, taking into account the contribution of both direct N2O and CO2 emissions, values of 0.069 kg(CO2),(eq) kg(bCOD)(-1), 0.008 kg(CO2),(eq) kg(bCOD)(-1) and 0.00022 kg(CO2,eq) kg(bCOD)(-1), were found for the net CFP of the aerated compartment, the disinfection unit and the clarifier, respectively.The plant energy Footprint (eFP) was also evaluated, confirming that the aeration systemis the major contributor to energy consumption, as well as to indirect CO2 emission, with a specific eFP of 1.49 kWh kg(bCOD)(-1). (C) 2018 Elsevier B.V. All rights reserved.
机译:水资源回收设施(WRRF)是气候变化和空气污染的源头,因为它们是直接和间接排放温室气体(GHG)的人为潜在来源。关于监测和核算WRRF温室气体排放的研究越来越引起人们的兴趣。在这项研究中,用于气体收集的浮动罩技术与废气法结合在一起,用于监测和分配市政水资源回收设施中充气和非充气罐中的一氧化二氮(N2O)和二氧化碳(CO2)排放,以调查其碳足迹(CFP)。据我们所知,这是首次将腔室技术用于评估沉降器的气体通量,其排放因子(EF)为4.71 * 10(-5)kg(CO2,eq)kg(bCOD)(- 1)被发现。在消毒装置中发现了有趣的结果,该消毒装置是直接N2O排放的主要贡献者(比排放因子为0.008 kg(CO2,eq)kg(bCOD)(-1)),这是由于羟胺与消毒剂(次氯酸盐)。生物曝气池的比排放因子为0.00112 kg(CO2,eq)kg(bCOD)(-1)。活性污泥池的平均直接CO2排放量等于0.068 kg(CO2)kg(bCOD)(-1),二级澄清池的平均直接CO2排放量等于0.00017 kg(CO2)kg(bCOD)(-1)。因此,考虑到直接N2O和CO2排放的贡献,值分别为0.069 kg(CO2),(eq)kg(bCOD)(-1),0.008 kg(CO2),(eq)kg(bCOD)(- 1)和曝气室,消毒装置和净化器的净CFP分别为0.00022 kg(CO2,eq)kg(bCOD)(-1),还评估了植物能量足迹(eFP),确认曝气系统是能源消耗以及间接CO2排放的主要贡献者,其特定eFP为1.49 kWh kg(bCOD)(-1)。 (C)2018 Elsevier B.V.保留所有权利。

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