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NO formation Tendency Characterization for Biomass Fuels

机译:生物质燃料的NO形成趋势表征

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When a solid fuel, such as coal, biomass or a mixture of these fuels, enters a hot fluidized bed, the volatile carbon and nitrogen compounds are released, while some nitrogen and carbon remains in the solid char. Volatile nitrogen can form reactive species such as NH_3, HCN and tar-nitrogen. These can react in the presence of oxygen to NO (and some N_2O). Some part of volatile nitrogen is always reduced to N_2. During combustion of the char residue, some part of the char-nitrogen forms NO (or N_2O) and the rest is converted to N_2. Usually the standard fuel analysis is not enough to allow for accurate NO emission predictions in large scale fluidized bed combustion. This paper presents NO formation tendency characterization results from novel laboratory measurements in a small-scale fluidised bed combustor. The laboratory results of this paper give a good insight into the distribution of fuel nitrogen between reactive and non-reactive (N_2) volatile components and char-nitrogen. A NO formation tendency database is formed based on the results, including data on biomass-, waste-, peat- and coal-type fuels. The combustion test results show that the cumulative conversion of fuel nitrogen to NO under lean, non-staged fluidized bed combustion is 20 - 50 % (850℃ with O_2 in excess). For biomass and peat, nearly all reactive nitrogen (forming NO) is released from the fuel during pyrolysis. NO formation during char combustion is significant with coal. With the help of the database, a reasonable estimate of the maximum non-staged NO emission in fluidized bed combustion can be obtained. Normally, air staging is utilized to reduce NO emissions. Effects of air-staging can be studied by means of modelling. In case of a BFBC boiler, the data can be used as input in the design or modelling of air staging for freeboard. For CFBC, the data can be used as input in the NO prediction where the once formed NO is further reduced by char carbon.
机译:当诸如煤,生物质或这些燃料的混合物的固体燃料进入热流化床时,挥发性碳和氮化合物被释放,而一些氮和碳保留在固体炭中。挥发性氮可以形成反应性物质,例如NH_3,HCN和焦油-氮。它们可以在氧气存在下反应成NO(和一些N_2O)。挥发性氮的某些部分总是还原为N_2。在焦炭残渣燃烧期间,一部分炭氮形成NO(或N_2O),其余转化为N_2。通常,标准燃料分析不足以在大规模流化床燃烧中提供准确的NO排放预测。本文介绍了在小型流化床燃烧器中通过新颖的实验室测量得出的NO形成趋势表征结果。本文的实验室结果很好地了解了反应性和非反应性(N_2)挥发性组分与炭氮之间燃料氮的分布。根据结果​​形成NO形成趋势数据库,包括有关生物质,废物,泥煤和煤类燃料的数据。燃烧试验结果表明,在稀薄,无段流化床燃烧条件下,燃料氮向NO的累积转化率为20-50%(850℃,O_2过量)。对于生物质和泥炭,热解过程中几乎所有的反应性氮(形成NO)都会从燃料中释放出来。煤在焦炭燃烧过程中不会形成大量NO。借助该数据库,可以获得对流化床燃烧中最大的非分级NO排放的合理估计。通常,空气分级用于减少NO排放。空气分段的影响可以通过建模来研究。对于高炉锅炉,该数据可以用作干舷空气分级设计或建模中的输入。对于CFBC,该数据可用作NO预测的输入,其中曾经形成的NO会进一步被炭碳还原。

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