the coking properties of coal at elevated pressures. - Argonne ...
the coking properties of coal at elevated pressures. - Argonne ... the coking properties of coal at elevated pressures. - Argonne ...
Two-Stage Combustion Staged combustion has been proposed as a means of reducing NO from an AFBc unit. Several investigators [2, 3, and 41 have conducted tests to'quantify the NO reduction with staging. However, these tests were run in small units and only overall effects were measured. To aid in evaluating the effect of staging on NO reduction and performance variables, the 6' x 6' AFBC facility was modified to aylow air injection at an elevation of 96 inches above the distributor plate. This elevation was chosen based on data from previous tests [21. Two injection ports -- on opposite walls of the unit -- were installed with valves to control flow and an orifice to measure flow. Tests were conducted at the conditions listed in Table 3. ConditionIVariable Bed Temp, *F Bed Height - inches Table 3 Summary of Operating Conditions and Measured Performance Variables Superficial Velocity - ftlsec Coal Feed - lblhr CaIS Ratio Recycle - lblhr In-Bed Air Flov - lblhr Overbed Air Plov - lblhr Flue Gas o2 - x SO2 - ppm CO - ppm NOx - ppm Sulfur Capture - 2 Combustion Efficiency - I - la 1564 51.8 7.3 1887 2.7 2560 19500 2.9 0 170 208 416 91.6 98.1 - Ib 1546 52.5 8.0 2042 2.7 2680 21500 0 2.9 265 185 372 86.1 97.4 Test - 2a - 1544 1547 50.0 49.8 7.1 7.1 2070 2064 2.1 2.5 2800 2920 19400 19400 2300 2300 2.9 562 247 195 77.1 96.8 - 2b 3.1 527 203 175 75.1 96.7 - 3a 1512 47.7 6.5 2192 2.7 2280 18300 4850 2.9 46 1 248 88 74.9 96.0 - 3b 1553 47.8 7.0 2228 2.5 2280 18900 4670 At each test condition, gas traverses were made at six heights along the centerline of the unit. The gas concentration profiles obtained in-bed (16 inches above the distributor plate) are shown on Figure 17. Note the peak in O2 and the drop in other gas concentrations near the 36-inch insertion depth. This is probably due to the recycle stream which is being injected with transport air at the 36-inch distance. Profiles above the bed (in the freeboard) were considerably more uniform. An integrated average of the profile obtained at each elevation was calculated. This average was then plotted versus distance above the distributor plate for CO, SO2, and NO as shown on Figures 18, 19, and 20. There are several points that are readily appzrent from these figures. 2.7 458 248 117 76. I 96.1 0 With zero overbed air, there is a significant reaction occurring in the freeboard, e.g., reduction of CO and NO X. 0 Two-stage combustion produces the expected trends in reducing NO while increasing SO2 and CO in the bed. 232
0 The addition of air at the 96-inch elevation allows further Combustion to occur in the freeboard, thus increasing SO2 and reducing CO and NOx. 0 Reducing the NOx level in the bed reduces NOx throughout the process. 0 Gas concentrations measured at the 240-inch elevation, using the freeboard sampling system and analysers, agree remarkably well with the similar, but completely separate, furnace outlet system and analysers. Figure 21 shows a plot of the furnace outlet NO and SO gas concentrations at 2 the three test conditions -- 0%, lo%, and 20% overbe8 air. CONCLUDING REMARKS Twenty-three test series have been completed on the 6' x 6' AFBC Development Facility covering over 7100 hours of operation. Data obtained thus far have clearly shown that fly ash recycle can improve combustion efficiency to the level needed for commercial operation. Recycle also improves sorbent utilization, thus reducing the limestone needed for sulfur capture. Measured NO emission levels from the 6' x 6' AFBC unit are well below current EPA limits. Howgver, two-stage combustion tests have shown that NO can be reduced to about 0.15 lb/million Btu. Additional work needs to be complered to improve Sulfur capture and combustion efficiency with two-stage combustion. Information obtained thus far has allowed a significant improvement in our understanding of the AFBC process and should prove useful to researchers in this field. Further, design of prototype hardware and other equipment developed and tested on the 6' x 6' should prove useful for commercial design. REFERENCES (11 G. A. Hammons and A. Skoop, "NO Formation and Control in Fluidized Bed Coal Combustion Processes," presentea at the ASME Winter Annual Meeting, Washington, DC; November 28 - December 2, 1971. [2] J. Tatebayashi, Y. Okada, K. Yano, and S. Ikeda, ."Simultaneous NO and SO2 Emission Reduction With Fluidized Bed Combustion", 6th Internatiogal Conference on Fluidized Bed Combustion, Atlanta, GA; April 1980. 131 T. Hirama, M. Tomita, T. Adachi, and M. Horio, "An Experimental Study for Low NO Fluidized-Bed Combustor Development 2 - Performance of Two Stage FlEidized-Bed Combustion"; EST, Vol. 14, No. 88; pp. 960-965. [4] T. E. Taylor, "NO Control Through Staged Combustion in Fluidized Bed Combustion Systemg", 6th International Conference on Fluidized Bed Combustion, Atlanta, GA; April 1980. 233
- Page 181 and 182: FIG 9. Limestone bed material alter
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- Page 271 and 272: could not be assumed constant. Thus
- Page 273 and 274: \ greatly acknowledged. Literature
- Page 275 and 276: constructed and operated to demonst
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- Page 279 and 280: atmospheric pressure fluidized bed
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Two-Stage Combustion<br />
Staged combustion has been proposed as a means <strong>of</strong> reducing NO from an AFBc<br />
unit. Several investig<strong>at</strong>ors [2, 3, and 41 have conducted tests to'quantify <strong>the</strong> NO<br />
reduction with staging. However, <strong>the</strong>se tests were run in small units and only<br />
overall effects were measured. To aid in evalu<strong>at</strong>ing <strong>the</strong> effect <strong>of</strong> staging on NO<br />
reduction and performance variables, <strong>the</strong> 6' x 6' AFBC facility was modified to aylow<br />
air injection <strong>at</strong> an elev<strong>at</strong>ion <strong>of</strong> 96 inches above <strong>the</strong> distributor pl<strong>at</strong>e. This<br />
elev<strong>at</strong>ion was chosen based on d<strong>at</strong>a from previous tests [21. Two injection ports --<br />
on opposite walls <strong>of</strong> <strong>the</strong> unit -- were installed with valves to control flow and an<br />
orifice to measure flow.<br />
Tests were conducted <strong>at</strong> <strong>the</strong> conditions listed in Table 3.<br />
ConditionIVariable<br />
Bed Temp, *F<br />
Bed Height - inches<br />
Table 3<br />
Summary <strong>of</strong> Oper<strong>at</strong>ing Conditions and Measured Performance Variables<br />
Superficial Velocity - ftlsec<br />
Coal Feed - lblhr<br />
CaIS R<strong>at</strong>io<br />
Recycle - lblhr<br />
In-Bed Air Flov - lblhr<br />
Overbed Air Plov - lblhr<br />
Flue Gas<br />
o2 - x<br />
SO2 - ppm<br />
CO - ppm<br />
NOx - ppm<br />
Sulfur Capture - 2<br />
Combustion Efficiency - I<br />
- la<br />
1564<br />
51.8<br />
7.3<br />
1887<br />
2.7<br />
2560<br />
19500<br />
2.9<br />
0<br />
170<br />
208<br />
416<br />
91.6<br />
98.1<br />
- Ib<br />
1546<br />
52.5<br />
8.0<br />
2042<br />
2.7<br />
2680<br />
21500<br />
0<br />
2.9<br />
265<br />
185<br />
372<br />
86.1<br />
97.4<br />
Test<br />
- 2a -<br />
1544 1547<br />
50.0 49.8<br />
7.1 7.1<br />
2070 2064<br />
2.1 2.5<br />
2800 2920<br />
19400 19400<br />
2300 2300<br />
2.9<br />
562<br />
247<br />
195<br />
77.1<br />
96.8<br />
- 2b<br />
3.1<br />
527<br />
203<br />
175<br />
75.1<br />
96.7<br />
- 3a<br />
1512<br />
47.7<br />
6.5<br />
2192<br />
2.7<br />
2280<br />
18300<br />
4850<br />
2.9<br />
46 1<br />
248<br />
88<br />
74.9<br />
96.0<br />
- 3b<br />
1553<br />
47.8<br />
7.0<br />
2228<br />
2.5<br />
2280<br />
18900<br />
4670<br />
At each test condition, gas traverses were made <strong>at</strong> six heights along <strong>the</strong><br />
centerline <strong>of</strong> <strong>the</strong> unit. The gas concentr<strong>at</strong>ion pr<strong>of</strong>iles obtained in-bed (16 inches<br />
above <strong>the</strong> distributor pl<strong>at</strong>e) are shown on Figure 17. Note <strong>the</strong> peak in O2 and <strong>the</strong><br />
drop in o<strong>the</strong>r gas concentr<strong>at</strong>ions near <strong>the</strong> 36-inch insertion depth. This is probably<br />
due to <strong>the</strong> recycle stream which is being injected with transport air <strong>at</strong> <strong>the</strong> 36-inch<br />
distance. Pr<strong>of</strong>iles above <strong>the</strong> bed (in <strong>the</strong> freeboard) were considerably more uniform.<br />
An integr<strong>at</strong>ed average <strong>of</strong> <strong>the</strong> pr<strong>of</strong>ile obtained <strong>at</strong> each elev<strong>at</strong>ion was calcul<strong>at</strong>ed.<br />
This average was <strong>the</strong>n plotted versus distance above <strong>the</strong> distributor pl<strong>at</strong>e for CO,<br />
SO2, and NO as shown on Figures 18, 19, and 20. There are several points th<strong>at</strong> are<br />
readily appzrent from <strong>the</strong>se figures.<br />
2.7<br />
458<br />
248<br />
117<br />
76. I<br />
96.1<br />
0 With zero overbed air, <strong>the</strong>re is a significant reaction occurring in<br />
<strong>the</strong> freeboard, e.g., reduction <strong>of</strong> CO and NO<br />
X.<br />
0 Two-stage combustion produces <strong>the</strong> expected trends in reducing NO<br />
while increasing SO2 and CO in <strong>the</strong> bed.<br />
232