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Study on the Effects of Iron and Arsenic on Particle Formation in a Diffusion Flame

机译:铁和砷对扩散火焰中颗粒形成的影响研究

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Iron pentacarbonyl and cacodylic acid(C_2H_7AsO_2) were added to a co-centric diffusion burner flame burning in a co-flowing stream of air. The basic fuel was a mixture of acetylene and ethylene. Liquid iron pentacarbonyl was vaporized by passing ethylene through it and was loaded into the flame. Cacodylic acid(C_2H_7AsO_2) was dissolved in a waterbed and was novelized by using a Venturi nozzle and Ar gas. The novelized arsenic compound was introduced into the diffusion dryer to get rid of water and it was introduced into the flame. Samples of aerosols and gaseous species were collected within the flames and also above the flames with filters and sampling bottle, and soot volume fraction through the flame was calculated with laser light extinction measurements. Aerosol was collected isokinetically also in the Inhalation chamber to measure particle concentration and size distribution. Laser extinction measurement showed that iron(Fe) gave an effect on soot formation process due to nucli and soot particle oxidation reactions, but arsenic did not make any role in soot particle oxidation reaction. FE-SEM of the aerosol sample showed that soot particle size for the iron doped flame was relatively smaller than one of non-iron doped flame, however one for the arsenic flame was even bigger than that of the pure hydrocarbon flame. Equilibrium products and temperature of stoichiometric mixture fraction were calculated with STANJAN Code for the iron and arsenic doped flames. The iron oxide of FeO(g) was found from mixture fraction of 0.1 and remained a dominant iron species between the reaction zone and near the fuel lean side. Fe_2O_3 started to appear near reaction and remained a dominant iron oxidized form through out the fuel lean side of the flame. The stoichiometric mixture fraction for the arsenic flame was 0.209. Elemental arsenic was found to be the dominant equilibrium form of arsenic in the fuel-rich part of the flame, either as atomic arsenic or as the allotrope As4.
机译:将五羰基铁和草酸(C_2H_7AsO_2)添加到同心扩散燃烧器中,在同流的空气流中燃烧。基本燃料是乙炔和乙烯的混合物。通过使乙烯通过使五羰基铁液体蒸发,然后将其装入火焰中。将水杨酸(C_2H_7AsO_2)溶解在水床上,并使用文丘里喷嘴和Ar气进行新颖化处理。将新型砷化合物引入扩散干燥器中以除水,然后将其引入火焰中。使用过滤器和采样瓶在火焰内以及火焰上方收集气溶胶和气态样品,并通过激光消光测量计算通过火焰的烟灰体积分数。也在吸入室内等速地收集气雾剂以测量颗粒浓度和尺寸分布。激光消光测量表明,铁(Fe)由于核素和烟灰颗粒的氧化反应而对烟灰形成过程产生了影响,但是砷在烟灰颗粒的氧化反应中没有任何作用。气溶胶样品的FE-SEM显示,掺铁火焰的烟尘粒径相对小于非掺铁火焰的烟尘粒径,但是砷火焰的烟尘粒径甚至比纯烃火焰的烟尘粒径还要大。用STANJAN代码计算出掺铁和砷的火焰的平衡产物和化学计量混合分数的温度。 FeO(g)的氧化铁是从0.1的混合比中发现的,并且仍然是反应区和稀燃料侧附近的主要铁物种。 Fe_2O_3开始出现在反应附近,并在火焰的贫燃料侧保持主要的铁氧化形式。砷火焰的化学计量混合物分数为0.209。发现元素砷是火焰中富含燃料的部分中砷的主要平衡形式,无论是原子砷还是同素异形体As4。

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