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Nonchemical Conditioning of Simulated Coal Gasification Streams Prior to Real-Time Hg Determinations Using Atomic Absorption

机译:采用原子吸收实时HG测定在实时HG测定之前的模拟煤气化流的非化学条件

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An experimental Hg CEM intended for use at coal gasification plants was developed and tested in the laboratory. The CEM uses atomic absorption (AA) with a deuterium-based background correction system. Prior to the Hg analyzer, aromatic hydrocarbons and ammonia (NH_3) are removed by catalytic oxidation with platinum (Pt). The Pt catalyst effectively removed heavy tars from a slipstream in field tests at a gasification facility. The catalyst also effectively destroyed NH_3 and light aromatic hydrocarbons from gas streams in the laboratory, and was able to pass low levels of elemental Hg in air. Full Hg recoveries were still obtained when using a simulated gasifier stream, but 25% of the Hg was in the oxidized form when HCl was present, even when using a pyrolytic converter downstream from the catalyst. HgCl_2 in air was effectively converted to elemental Hg with a pyrolyzer, and little or no reoxidation of Hg occurred as the gases cooled. However, when HCl was also present, results indicated that Hg oxidation downstream from the pyrolyzer is of concern. When simulated gasifier streams were passed over the catalyst, various aerosols and solid condensates formed as the gases cooled. The amount and composition of the aerosols and condensates depended on various experimental parameters. Even under optimal conditions, white aerosols were observed exiting the catalyst tube. Those aerosols formed easily in the presence of a catalyst and appeared to be H_2SO_4 mist from the oxidation of H_2S. After the catalyst, a Nafion-based dryer is used for moisture removal. Low levels of elemental Hg (in air) could be successfully transported through a laboratory-scale Nafion dryer, while 15-20% of the Hg was lost when passing the gases through a field-scale Nafion-based dryer. Sample gas flow rate was an important variable.
机译:在实验室开发并测试旨在用于煤气化植物的实验HG CEM。 CEM使用具有基于氘的背景校正系统的原子吸收(AA)。在HG分析仪之前,通过用铂(Pt)通过催化氧化除去芳烃和氨(NH_3)。 PT催化剂在气化设施处的现场试验中有效地除去重质焦油。催化剂还有效地破坏了实验室中的气流中的NH_3和轻芳族烃,并且能够在空气中通过低水平的元素Hg。使用模拟气化器流时仍然获得全HG回收,但是,当存在HCl时,25%的Hg在存在HCl时,即使在催化剂下游的热解转换器时也是如此。空气中的HgCl_2有效地用热解器转化为元素Hg,并且在气体冷却时几乎没有Hg的再氧化。然而,当HCl也存在时,结果表明,从热解器下游的Hg氧化是关注的。当模拟气化器流通过催化剂时,随着冷却的气体而形成的各种气溶胶和固体缩合物。气溶胶和缩合物的量和组成依赖于各种实验参数。即使在最佳条件下,观察到催化剂管的白色气溶胶。这些气溶胶在催化剂存在下容易形成,并且从H_2S的氧化似乎是H_2SO_4雾。在催化剂之后,使用基于Nafion的干燥器用于水分去除。低水平的元素Hg(空气中)可以通过实验室级的无限干燥器成功地运输,而在通过气体通过现场级别的基于Nafion基干燥器时,15-20%的Hg损失。样品气体流速是一个重要的变量。

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