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a study on the calcination and sulfation behavior of limestone during ...

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Juan chen et al.<br />

flame <strong>during</strong> coal combusti<strong>on</strong>, which substantially increased <strong>the</strong> limest<strong>on</strong>e particle<br />

temperature to a level overweighing <strong>the</strong> inhibitory effect <strong>of</strong> CO2 partial pressure. As can<br />

be seen in fig. 2, adding 18% CaCO3 to coal combusted in DTF, increased <strong>the</strong> limest<strong>on</strong>e<br />

particle temperature from 1183 K to 1223 K in O2/CO2 <strong>and</strong> 1194 K in air.<br />

Unreacted CaCO3, %<br />

20<br />

15<br />

10<br />

5<br />

0<br />

Air<br />

Oxy-fuel (a)<br />

18% 5% 1%<br />

Mass percentage <strong>of</strong> CaCO3 in coal<br />

Unreacted CaCO3, %<br />

20<br />

15<br />

10<br />

5<br />

0<br />

Air+SO2<br />

Oxy-fuel+SO2 (b)<br />

18% 5% 1%<br />

Mass percentage <strong>of</strong> CaCO3 in coal<br />

Fig 3Variati<strong>on</strong> <strong>of</strong> <strong>the</strong> fracti<strong>on</strong>s <strong>of</strong> unreacted limest<strong>on</strong>e with <strong>the</strong> additi<strong>on</strong> <strong>of</strong> limest<strong>on</strong>e<br />

The mass ratio <strong>of</strong> limest<strong>on</strong>e to ash in coal <strong>and</strong> <strong>the</strong> c<strong>on</strong>centrati<strong>on</strong> <strong>of</strong> SO2 in flue gas were<br />

also c<strong>on</strong>firmed playing noticeable role <strong>on</strong> <strong>the</strong> extent <strong>of</strong> limest<strong>on</strong>e calcinati<strong>on</strong>. As<br />

dem<strong>on</strong>strated in fig. 3, in ei<strong>the</strong>r pure gas, air versus 27% O2/73% CO2 at a reactor<br />

length <strong>of</strong> 1200 mm in panel (a), with <strong>the</strong> decrease in <strong>the</strong> additi<strong>on</strong> percentage <strong>of</strong><br />

limest<strong>on</strong>e, i.e. increase in <strong>the</strong> mass ratio <strong>of</strong> coal ash/sulfur to limest<strong>on</strong>e, <strong>the</strong> fracti<strong>on</strong> <strong>of</strong><br />

unreacted CaCO3 was decreased drastically. If <strong>the</strong> reacti<strong>on</strong>s (1) <strong>and</strong> (2) shown above<br />

are <strong>the</strong> single routes for limest<strong>on</strong>e calcinati<strong>on</strong> <strong>and</strong> sulfati<strong>on</strong>, <strong>the</strong> presence <strong>of</strong> coal ash <strong>and</strong><br />

sulfur in <strong>the</strong> furnace should not affect <strong>the</strong> extent <strong>of</strong> <strong>the</strong> right shift <strong>of</strong> reacti<strong>on</strong> (1),<br />

because <strong>the</strong>y do not participant in this reacti<strong>on</strong>. The SO2 emitted from coal-bound<br />

sulphur is also insignificant, as <strong>the</strong> sulphur in coal <strong>on</strong>ly accounts for 0.9 wt%. It is thus<br />

referrable that ash (2.24% c<strong>on</strong>tent) plays <strong>the</strong> main role <strong>on</strong> <strong>the</strong> calcinati<strong>on</strong> extent <strong>of</strong><br />

limest<strong>on</strong>e. This clearly indicates <strong>the</strong> interacti<strong>on</strong> between limest<strong>on</strong>e <strong>and</strong> coal ash,<br />

according to <strong>the</strong> following reacti<strong>on</strong> (16) <strong>and</strong> (17), respectively.<br />

CaO+ Al O ⋅ SiO →CaO⋅<br />

Al O ⋅ SiO<br />

(16)<br />

2<br />

3<br />

2<br />

CaCO 3 + Al2O3<br />

⋅ SiO2<br />

→ CaO ⋅ Al2O3<br />

⋅ SiO2<br />

+ CO2<br />

(17)<br />

The Ca-Al-Si formed could be shed away from limest<strong>on</strong>e surface, which in turn ensured<br />

<strong>the</strong> exposure <strong>of</strong> fresh surface <strong>of</strong> limest<strong>on</strong>e to undergo decompositi<strong>on</strong> <strong>and</strong> react with SO2.<br />

The directi<strong>on</strong> reacti<strong>on</strong> (17) should occur slowly in O2/CO2 with high CO2 partial<br />

pressure when compared with <strong>the</strong> interacti<strong>on</strong> (16) between calcium oxide (derived from<br />

limest<strong>on</strong>e calcinati<strong>on</strong>) <strong>and</strong> coal ash which is predominant in air (Zhang et al, 2002), as<br />

indicated by <strong>the</strong> c<strong>on</strong>stantly higher unreacted CaCO3 fracti<strong>on</strong> over <strong>the</strong> mass ratio <strong>of</strong><br />

limest<strong>on</strong>e to coal in O2/CO2 than in air. Moreover, as suggested by <strong>the</strong> results for adding<br />

1000 ppmV SO2 in fig. 3(b), it is clear that <strong>the</strong> un-reacted limest<strong>on</strong>e fracti<strong>on</strong> was<br />

reduced quickly with <strong>the</strong> additi<strong>on</strong> <strong>of</strong> SO2 compared to that without SO2 additi<strong>on</strong> in<br />

panel (a). The limest<strong>on</strong>e calcinati<strong>on</strong> extent in O2/CO2 was even increased to <strong>the</strong> similar<br />

level with that obtained in air. This is a clear reflecti<strong>on</strong> <strong>of</strong> <strong>the</strong> importance <strong>of</strong> <strong>the</strong> direct<br />

sulfati<strong>on</strong> reacti<strong>on</strong> (3) at high SO2 c<strong>on</strong>centrati<strong>on</strong> in an oxy-fuel boiler.<br />

2<br />

3<br />

2<br />

6

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