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 ...

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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

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

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