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 ...
ottom of the bed, and steam-carbon gasification and water gas shift reaction in a single perfectly mixed isothermal stage. The model is significant in and of itself, but it6 particular importance to the project is that it enables the specification of gasifier conditions required to produce a feed to the acid gas removal system with a predetermined flow rate and composition. In a previous report (Ferrell et al., 19811, the structure of the model was presented, and the ability of the model to correlate data on the gasification of a devolatilized bituminous coal was demonstrated. The model was subsequently extended to include the evolution of volatile gases in the pyrolysis stage of the gasification process, and used to fit the data from the present series of runs with the New Mexico subbituminous coal. The model takes as input the average reactor bed temperature and pressure, the bed dimensions, feed rates of coal, steam, oxygen, and nitrogen, solids holdup in the bed, and ultimate analysis of the feed coal, and calculates carbon conversion and make gas flow rate and composition. A complete description of the model in its present form will be given in an EPA report now in preparation. A lot of model predictions vs measured values of carbon conversion is shown in Figure 2. The reasonably close proximity of most points to the 45 degree line on this and similar plots for total make gas flow rate and individual species (CO, H2, COP) emissions is gratifying io view of the simplicity of the model. AGRS OPERATION AND RESULTS Top feeding coal into the gasifier allows a substantial amount of devolatilization to take place before the coal enters the fluidized bed. While most commercial fluidized bed gasifiers will use a deep-bed injection method of feeding coal into the fluidized bed, it was decided not to modify our system in order to maximize the formation of tars, oils, and other hydrocarbons and to provide a more complete test of the AGRS. It should also be noted that the relatively simple acid gas removal system used in this study lacks the complexity of the selective systems found in many physical absorption processes. These systems, which use more than one absorber and stripper, and often several flash tanks, separate sulfur gases from carbon dioxide before further processing of the acid gas. This is done to concentrate the sulfur gases before they are fed to a sulfur recovery unit, and to recover the Cog or vent the C02-rich stream to the atmosphere. While the AGRS used in this study could have been modified to emulate an existing selective absorption process, it was decided that data obtained from a relatively simple but well-characterized system would be of more use than data obtained from a fairly complex system, similar but not identical, to existing commercial systems. Through judicious use of computer simulation and engineering calculations, the data obtained from our system should be extrapolatable to more industrially significant situations. 100
', Complete results from all runs carried out will be -published in a forthcoming EPA report. Illustrative results from a single run will be Presented here. Gas analyses from the six different locations shown in Figure 1 are given in Table 2. The paragraphs that follow Summarize the Principal conclusions derived from analyses of the run data. B Ci3 '2'4 C2H6 H S c8s N co c44 Benzene Toluene Ethyl Benz. Xylenes * Thiopiene Pro pang Butane ** Methanol Acid Gas Removal 31.60 23.51 0.52 0.72 0.250 0.0078 19.36 6.56 17.29 0.087 0.031 0.0016 0.0080 44 16 TRACE TRACE 1505 208 185 ----- 31 .ll 23.91 0.53 0.72 0.284 0.0076 19.61 6.46 17.47 0.097 0.034 0.0017 0.0094 44 29 ----- 3 1521 198 150 ----- 31.29 21.98 0.56 0.76 0.287 0.0076 19.93 6.51 17.92 0.234 0.534 0.0450 0.1557 127 28 8 TRACE 1811 253 143 -..--- 42.38 -___ 0.0242 0.0164 0.0048 0.0001 26.79 7.54 23.35 TRACE 0.0054 ---- --___ TRACE ----- I___ TRACE 107 301 54 ----- 15.58 25.99 1.28 1.92 0.090 0.0041 19.27 14.20 21.55 0.0031 0.0033 _-_-- ---- -I-- 5 ----- TRACE 995 172 91 ----- 0.00 64.74 1.54 2.13 0.66 0.027 23.06 2.36 1 .80 0.15 0.030 ----- --___ ----- TRACE ----- TRACE 4640 2203 71 3.68 The primary function of the AGRS is to remove COP and sulfur compounds from the gases produced during coal gasification. When using refrigerated methanol, the absorber also acts as an excellent trap for any other compound which condenses or disolves in the methanol at absorber conditions. The run data show that for the range of conditions studied, the most significant factor in high acid gas removal efficiencies is stripping efficiency. With the use of more extreme operating conditions and "cleaner" methanol fed to the absorber, the levels of C02, COS and H2S in the sweet gas can be reduced to acceptable levels. This is a particularly important point in the case of COS removal which poses 101
- Page 50 and 51: COAL PYROLYSIS AT HIGH TEMPERATURES
- Page 52 and 53: actions, decreasing the secondary c
- Page 54 and 55: 01 40 60 TI MEISeC) 80 100 120 140
- Page 56 and 57: Reaction Temperature OC In-situ Ini
- Page 58 and 59: and the gas velocity is often repre
- Page 60 and 61: The mathematical model developed he
- Page 62 and 63: si sio Fraction of solid species i
- Page 64 and 65: Table 2. Differential Equations Mod
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- Page 68 and 69: to condense excess steam, the press
- Page 70 and 71: conversion-time data.* The integrat
- Page 72 and 73: catalyzed and uncatalyzed runs were
- Page 74 and 75: CATALYTIC EFFECTS OF ALKALI METAL S
- Page 76 and 77: %me thermogravimetric measurements
- Page 78 and 79: than in steam. Figure 9 shows data
- Page 80 and 81: C - C02 REACTION C - H20 REACTION L
- Page 82 and 83: 1. 2. 3. 4. 5. 6. 7. 8. 9. 10. 11.
- Page 84 and 85: n 'm L u. t m - L 84
- Page 87 and 88: i 5360-096bw \ KINETICS OF POTASSIU
- Page 89 and 90: t 5360-096pj There is an interactio
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- Page 93 and 94: I 1. I 5360-096bw ranging from atmo
- Page 95 and 96: uY.ku ICHlMAlIC OF MINI-FLUID BE0 R
- Page 97 and 98: 800-12-1133 -9 FIGURE IO CALCULATED
- Page 99: Mexico coal. Table 1 shows an analy
- Page 103 and 104: I the methanol down to atmospheric
- Page 105 and 106: TABLE 3 -----______________________
- Page 107 and 108: \ "I N z 107 c. . 0 0
- Page 109 and 110: I. INTRODUCTION DIRECT METHANATION
- Page 111 and 112: The catalyst development program fo
- Page 113 and 114: Preparing process flow diagrams and
- Page 115 and 116: \ \ i 1. 2,000 4,000 6,000 8,000 10
- Page 117 and 118: (JMS-OlBM-2). The mass spectra were
- Page 119 and 120: I I Fairbridge, R.W. (ed.) 1972, En
- Page 121 and 122: v- W V z d 3 z m 4 ? P m W c3 W m N
- Page 123 and 124: e. \ I , W 2 m 4 t- CI 99-79 noooo
- Page 125 and 126: L Table I: Compositions of High Tem
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- Page 129 and 130: 4 , 1024 1024 3a 3b J Mineral Parti
- Page 131 and 132: The Determination of Mineral Distri
- Page 133 and 134: pyrite crystals in framboids locate
- Page 135 and 136: FIG. 1. TEM MICROGRAPH OF A HIGH VO
- Page 137 and 138: \ \ FIG. 5. SEM MICROGRAPH SHOWING
- Page 139 and 140: \ , species. In fact, combustion ex
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- Page 143 and 144: \ i SURFACE AND BULK ENRICHMENT OF
- Page 145 and 146: I Coal Ash Sintering Model and the
- Page 147 and 148: 5 carried out such sintering measur
- Page 149 and 150: I this ash and other bituminous coa
ottom <strong>of</strong> <strong>the</strong> bed, and steam-carbon gasific<strong>at</strong>ion and w<strong>at</strong>er gas shift<br />
reaction in a single perfectly mixed iso<strong>the</strong>rmal stage. The model is<br />
significant in and <strong>of</strong> itself, but it6 particular importance to <strong>the</strong><br />
project is th<strong>at</strong> it enables <strong>the</strong> specific<strong>at</strong>ion <strong>of</strong> gasifier conditions<br />
required to produce a feed to <strong>the</strong> acid gas removal system with a<br />
predetermined flow r<strong>at</strong>e and composition.<br />
In a previous report (Ferrell et al., 19811, <strong>the</strong> structure <strong>of</strong> <strong>the</strong><br />
model was presented, and <strong>the</strong> ability <strong>of</strong> <strong>the</strong> model to correl<strong>at</strong>e d<strong>at</strong>a on<br />
<strong>the</strong> gasific<strong>at</strong>ion <strong>of</strong> a devol<strong>at</strong>ilized bituminous <strong>coal</strong> was demonstr<strong>at</strong>ed.<br />
The model was subsequently extended to include <strong>the</strong> evolution <strong>of</strong> vol<strong>at</strong>ile<br />
gases in <strong>the</strong> pyrolysis stage <strong>of</strong> <strong>the</strong> gasific<strong>at</strong>ion process, and used to fit<br />
<strong>the</strong> d<strong>at</strong>a from <strong>the</strong> present series <strong>of</strong> runs with <strong>the</strong> New Mexico<br />
subbituminous <strong>coal</strong>. The model takes as input <strong>the</strong> average reactor bed<br />
temper<strong>at</strong>ure and pressure, <strong>the</strong> bed dimensions, feed r<strong>at</strong>es <strong>of</strong> <strong>coal</strong>, steam,<br />
oxygen, and nitrogen, solids holdup in <strong>the</strong> bed, and ultim<strong>at</strong>e analysis <strong>of</strong><br />
<strong>the</strong> feed <strong>coal</strong>, and calcul<strong>at</strong>es carbon conversion and make gas flow r<strong>at</strong>e<br />
and composition. A complete description <strong>of</strong> <strong>the</strong> model in its present form<br />
will be given in an EPA report now in prepar<strong>at</strong>ion. A lot <strong>of</strong> model<br />
predictions vs measured values <strong>of</strong> carbon conversion is shown in Figure 2.<br />
The reasonably close proximity <strong>of</strong> most points to <strong>the</strong> 45 degree line on<br />
this and similar plots for total make gas flow r<strong>at</strong>e and individual<br />
species (CO, H2, COP) emissions is gr<strong>at</strong>ifying io view <strong>of</strong> <strong>the</strong> simplicity<br />
<strong>of</strong> <strong>the</strong> model.<br />
AGRS OPERATION AND RESULTS<br />
Top feeding <strong>coal</strong> into <strong>the</strong> gasifier allows a substantial amount <strong>of</strong><br />
devol<strong>at</strong>iliz<strong>at</strong>ion to take place before <strong>the</strong> <strong>coal</strong> enters <strong>the</strong> fluidized bed.<br />
While most commercial fluidized bed gasifiers will use a deep-bed<br />
injection method <strong>of</strong> feeding <strong>coal</strong> into <strong>the</strong> fluidized bed, it was decided<br />
not to modify our system in order to maximize <strong>the</strong> form<strong>at</strong>ion <strong>of</strong> tars,<br />
oils, and o<strong>the</strong>r hydrocarbons and to provide a more complete test <strong>of</strong> <strong>the</strong><br />
AGRS.<br />
It should also be noted th<strong>at</strong> <strong>the</strong> rel<strong>at</strong>ively simple acid gas removal<br />
system used in this study lacks <strong>the</strong> complexity <strong>of</strong> <strong>the</strong> selective systems<br />
found in many physical absorption processes. These systems, which use<br />
more than one absorber and stripper, and <strong>of</strong>ten several flash tanks,<br />
separ<strong>at</strong>e sulfur gases from carbon dioxide before fur<strong>the</strong>r processing <strong>of</strong><br />
<strong>the</strong> acid gas. This is done to concentr<strong>at</strong>e <strong>the</strong> sulfur gases before <strong>the</strong>y<br />
are fed to a sulfur recovery unit, and to recover <strong>the</strong> Cog or vent <strong>the</strong><br />
C02-rich stream to <strong>the</strong> <strong>at</strong>mosphere. While <strong>the</strong> AGRS used in this study<br />
could have been modified to emul<strong>at</strong>e an existing selective absorption<br />
process, it was decided th<strong>at</strong> d<strong>at</strong>a obtained from a rel<strong>at</strong>ively simple but<br />
well-characterized system would be <strong>of</strong> more use than d<strong>at</strong>a obtained from a<br />
fairly complex system, similar but not identical, to existing commercial<br />
systems. Through judicious use <strong>of</strong> computer simul<strong>at</strong>ion and engineering<br />
calcul<strong>at</strong>ions, <strong>the</strong> d<strong>at</strong>a obtained from our system should be extrapol<strong>at</strong>able<br />
to more industrially significant situ<strong>at</strong>ions.<br />
100