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On the Formation of Nitrogen Oxides During the Combustion of ...

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2.2 Theory <strong>of</strong> Exhaust Gas <strong>Formation</strong><br />

• NNH-intermediate route<br />

• Fuel nitrogen mechanism<br />

• <strong>Formation</strong> <strong>of</strong> NO 2<br />

<strong>Nitrogen</strong> dioxide (NO 2 ) is a reddish-brown toxic gas with a characteristically<br />

pungent odor. It is corrosive and highly oxidizing. Although <strong>the</strong> boiling point<br />

<strong>of</strong> NO 2 is high at T = 294K [453], its low partial pressure in <strong>the</strong> atmosphere<br />

prevents condensation. <strong>Nitrogen</strong> dioxide also has an uneven number <strong>of</strong> valence<br />

electrons and forms <strong>the</strong> dimer N 2 O 4 at higher concentrations and lower<br />

temperatures [391, 451]. For gas turbines <strong>of</strong> previous generations, characteristic<br />

NO 2 /NO x ratios were determined to be in <strong>the</strong> range <strong>of</strong> 15 to 50 %, with<br />

highest values prevailing under lean conditions or in idle mode. Yellow smoke<br />

was frequently encountered and seen as a formidable challenge in combustion<br />

engineering. The extensive formation <strong>of</strong> NO 2 was finally located in <strong>the</strong><br />

primary zone <strong>of</strong> <strong>the</strong> combustor [100, 229, 241, 248]. In typical modern combustion<br />

processes, NO 2 is emitted in small quantities <strong>of</strong> 5 to 10% by volume<br />

<strong>of</strong> <strong>the</strong> total NO x emissions along with NO, and it is formed in <strong>the</strong> atmosphere<br />

by <strong>the</strong> oxidation <strong>of</strong> NO [391, 451].<br />

In general, NO 2 is unlikely to be formed in a premixed flame under stoichiometric<br />

conditions. However, nonpremixed flames and/or local areas <strong>of</strong> lower<br />

temperature <strong>of</strong> 600 to 1200 K are conducive to NO 2 formation. Fur<strong>the</strong>rmore,<br />

<strong>the</strong> temperature level succeeding <strong>the</strong> initial combustion stages is essential, as<br />

NO 2 destruction is initiated at temperatures above 900 to 950 K due to equilibrium<br />

with NO [214] and <strong>the</strong> presence <strong>of</strong> <strong>the</strong> radicals O, H, and OH that play<br />

an important role in recombination reactions [229, 380]. Never<strong>the</strong>less, <strong>the</strong>re<br />

has been controversy surrounding <strong>the</strong> question to which extent <strong>the</strong> NO 2 measured<br />

in some experiments is due to <strong>the</strong> actual combustion process or to sample<br />

probe effects [15, 149, 241]. As summarized by Kramlich and Malte [217],<br />

combustor-formed NO 2 is believed to be due to <strong>the</strong> rapid cooling <strong>of</strong> pockets<br />

<strong>of</strong> combustion gases as <strong>the</strong>y turbulently mix with cooling air. This could also<br />

be demonstrated in measurements by a sharp increase in <strong>the</strong> NO 2 /NO x ratio<br />

while varying <strong>the</strong> equivalence ratio as well as parameters responsible for flame<br />

length and aerodynamic quenching [15, 69, 217].<br />

Nitrous oxide (N 2 O) is ubiquitous, even in <strong>the</strong> absence <strong>of</strong> any anthropogenic<br />

sources. It is nei<strong>the</strong>r known to be involved in photochemical smog reactions<br />

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