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FUEL NITROGEN CONVERSION DURING FUEL RICH COMBUSTION OF PULVERIZED COAL AND CHAR

机译:煤粉和煤焦的富燃料燃烧过程中的燃料氮转化

摘要

The conversion of coal and char nitrogen has been investigated during fuel rich combustion. The experiments were done with the objective of clarifying the roles of NO, HCN, and NH₃, and char nitrogen in the post-combustion gases in the first, fuel rich stage of a staged combustor. The experimental apparatus includes a downflow combustor of 15 cm internal diameter and 180 cm length constructed of fibrous alumina insulation surrounding a central tube composed of vacuum- formed alumina cylinders. The combustion gases and solids were sampled in situ with a water-cooled and -quenched probe. Neither the combustor nor the sample probe were found to be reactive towards NO. Temperatures of the gases and walls were measured with Type K thermocouples and the particle temperatures were determined with a seven wavelength infrared pyrometer. Gas compositions were measured chromatographically using a 5A molecular seive for permanent gases (H₂, O₂, N₂, CO, and CH₄) and Poropak T for polar gases (CO₂ and HCN). A chemiluminescent analyzer measured NO. NH₃ and HCN were measured in the quench water with ion electrodes. The C, H, N, ash compositions of the char were measured with an elemental analyzer. Experiments of the fuel rich conversion of char nitrogen show that at all stoichiometries (SR = 0.8, 0.4) the concentrations of HCN and NH₃ in the post-flame gases are small compared to the concentration of NO. Char nitrogen conversion was stoichiometric or greater. NO destruction was found to be controlled by a heterogeneous mechanism involving the char carbon surface. The mechanism is deactivated by oxygen, an effect demonstrated by others. The fuel rich conversion of coal nitrogen was investigated with a Utah bituminous coal. At moderate fuel rich conditions (SR = 0.8), the residual char nitrogen conversion is 90 percent or greater and NH₃ and HCN concentrations were less than 20 ppmv. NO peaked at 1200 ppmv (1850 K) and declined to 600 (1580 K) ppmv over 1.8 seconds. Coal nitrogen conversion is dominated by NO formation at this stoichiometry. At extreme fuel rich conditions (SR = 0.4), coal nitrogen conversion is 85 percent. The gas is dominated by HCN, NO, and NH₃. HCN decayed from 600 ppm to 300 ppmv, NO from 350 to 50, and NH₃ increased from 200 to 375 ppmv, indicating that interconversion reactions in the gas phase are dominating. The kinetics which govern the volatile nitrogen reactions can be described by global homogeneous kinetics as follows: UNFORMATTED TABLE/EQUATION FOLLOWS: r₁ = d/dt[HCN] = -5.5x10¹⁷ exp(-83.3 K/RT)[HCN][H₂O]/[H₂]¹/² mole/cm³s r₂ = d/dt[NO] = -2.2x10¹⁶ exp(-54.4 K/RT)[NO][NH₃]/[H₂]¹/² d/dt[NH₃] = d/dt[NO] - d/dt[HCN] UNFORMATTED TABLE/EQUATION ENDS These yield rates for free radical reactions very similar to those determined in gas flame experiments, lending credence to their validity. A one-dimensional combustor model has been formulated which accounts for the heterogeneous combustion and gasification of the coal and char. This model includes the devolatilization of the coal and homogeneous oxidation of carbon monoxide and devolatilized species. The water-gas shift reaction is assumed to be equilibrated. The model also includes the mass, momentum and energy balances of the particles but obviates the solution of the combustor heat balance by using the measured gas temperature in the solution. The model accurately predicts the gas and elemental conversions and particle temperatures observed in the experiments, and supports the homogeneous and heterogeneous kinetics of post-combustion fuel nitrogen conversion.
机译:已经研究了富燃料燃烧过程中煤和焦炭氮的转化。进行实验的目的是阐明在分级燃烧器的第一,富燃料阶段的后燃烧气体中NO,HCN和NH 3以及炭中的氮的作用。实验设备包括一个内径15厘米,长180厘米的下流燃烧室,该下流燃烧室由纤维状氧化铝绝缘材料构成,围绕着由真空成型的氧化铝圆柱体组成的中心管。用水冷淬火的探头对燃烧气体和固体进行原位采样。燃烧室和样品探针均未发现对NO有反应性。用K型热电偶测量气体和壁的温度,并用七波长红外高温计确定颗粒温度。使用5A分子筛对永久性气体(H 2,O 2,N 2,CO和CH 3)进行色谱分析,并对极性气体(CO 2和HCN)使用Poropak T进行色谱分析。化学发光分析仪测量NO。 NH 3和HCN是在带离子电极的淬灭水中测定的。用元素分析仪测量炭的C,H,N,灰分组成。焦炭富燃料转化实验表明,在所有化学计量比(SR = 0.8、0.4)下,与NO相比,燃烧后气体中HCN和NH 3的浓度都较小。炭氮转化率是化学计量的或更高。没有发现破坏是由涉及炭碳表面的异质机制控制的。氧气使该机制失活,其他人证明了这一作用。用犹他州的烟煤研究了煤氮的富燃料转化。在适度的富燃料条件下(SR = 0.8),残留的炭氮转化率为90%或更高,并且NH 3和HCN浓度小于20 ppmv。 NO在1.8秒内达到1200 ppmv(1850 K)的峰值,然后降至600(1580 K)ppmv。在该化学计量下,煤氮转化主要由NO的形成决定。在极端富燃料条件下(SR = 0.4),煤氮转化率为85%。气体主要由HCN,NO和NH 3组成。 HCN从600ppmv降至300ppmv,NO从350ppm降低至50ppmv,NH 3从200ppmv升高至375ppmv,表明气相中的相互转化反应占主导。支配挥发性氮反应的动力学可以用整体均匀动力学描述如下:未格式化的表格/方程式:r = d / dt [HCN] = -5.5x10 10 exp(-83.3 K / RT)[HCN] [H 2 O] / [H 2] 1/2摩尔/ cm 3 s r 2 = d / dt [NO] = -2.2x10 10⁶exp(-54.4 K / RT)[NO] [NH 3] / [H 2] 1/2 d / dt [NH 3] = d / dt [NO]-d / dt [HCN]未定型的表格/方程式末端这些自由基反应的产率与气体火焰实验确定的产率非常相似,从而证明了它们的有效性。已经建立了一维燃烧器模型,该模型考虑了煤和焦炭的不均匀燃烧和气化。该模型包括煤的脱挥发分,一氧化碳和脱挥发分物质的均相氧化。假定水煤气变换反应是平衡的。该模型还包括粒子的质量,动量和能量平衡,但通过使用溶液中测得的气体温度来消除燃烧器热平衡的解。该模型可准确预测实验中观察到的气体和元素转化率以及颗粒温度,并支持燃烧后燃料氮转化的均质和非均质动力学。

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