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 ...
Diminishing C-loss along with pressure rise is related to an increased 0 tration , whereas diminishing C-loss along with rising temperature is attr?b%?:i higher reaction velocity. Increasing fluidizing velocities reduce the residence time of the coal in the reactor and, thus, cause higher C-losses. If one found a means of extending this residence time -- be it by appropriate plant design or/and b coal preparation -- the specific heat release rate could be improved proportionate& to the fluidizing velocity. A longer residence time of the coal by means of increased bed height will diminish C-losses , too. C-loss may be influenced also by coal preparation measures. As shown on figure 3, the C-loss will, when fueling closely sized coal fractions, pass through a maximum as soon as the particle diameter approches the elutriation cut point. Coarse coal grains will remain in the bed up to the moment where they are burnt down to a size allowing their elutriution or preventing them from being recycled by the inertial separators. With sufficiently small fractions (coal dust) the reaction time is apparently shorter than the residence time in the reactor space so that the coal particles are almost completely burnt up. As far as industrial plants are concerned, the logical conclusion from this is to separate coal dust &om the coarser fractions and blow the dust pneumatically into the fluidized bed from below, in order to allow a maximum residence time of the dust and avoid erosion in the feed ducts, whereas the coarse fractions, being introduced from above, are allowed sufficient time to spread over the bed while being burnt up. In this case it can be taken from the diagrams, e.g. figure 3, where the preparation cut points for each specific plant are viz . which granular fraction should be separated and lor further comminuted. Examination of the carbon carry-over by means of screening for its size distribution does not yield accurate results since char aggregations will disintegrate. The results of figure 3 are, however, reconfirmed by this approximative evaluation. Moreover it can be verified from fly ash separation in two subsequent cyclones that the fine dust from the second cyclone is very low in carbon, whereas the "coarse dust" of the first one will always contain the bulk of the unburnt carbon. Apart from the determinable and adjustable operational parameters, C-loss is also a function of the specific plant parameters. Measuring data can best be reproduced in laboratory equipment. When doing so, one observes other and so far not measurable operational conditions which bear on the results. Among these have to be considered the size distribution of the fluidized bed ash particles which changes during opera- tion, or changing fluidity and cohesive properties of the bed ash when adding various gradations of limestone. A comparison of the C-loss measured in reactor no. 1 with that of the semi-technical Plant V (figure 5) -- the cross-section of the free-board has been enlarged in both units -- shows good coincidence. It should be borne in mind, however, that here varying particle gradations and bed heights compensate each other in a way not clearly identified so far. As was expected, there are differences also in the C-losses for the different laboratory reactor types since inertial separators are not optimized. This is not disturbing as long as feed materials, viz. types of limestone and coal, are compared by measurements in one reactor only. As soon as it comes to scaling up results, however, one has to know about the reasons and influences of specific operational conditions. 220
i \ ' 2.2. soz Emission and NOx Emission Statements on the pressure-dependences of SO and NO emissions (figure 2) are so far based on measurements of two pressure levels (13 and 4.5 bar). When moving to the higher pressure SO2 and NO emissions will be diminished by more than 50 %. The qualitative evaluations of ea%y orientation tests on the new pressure apparatus IV where measurements at several pressures between 1 and 10 bar are to be carried out, do reconfirm this improvement. Fi re 10 shows the stroig dependence of SO emissions on the size of the limestone *wed Ca/S ratio). It is, however, strhing and so far not explainable (figure 5) that varying sizes of one same type of limestone lead to different temperature dependencies. Dolomite shows a similar behaviour (figure 6). When adding coarse material, SO emission will slump with rising temperatures, whereas the opposite happens wgen material of small grain sizes is added. Excess air (figure 7) has a weak influence on SO2 emission, while its effect on NOx emission is strong since in this case the oxygen concentration is decisive for the conversion of that proportion of fuel-nitrogen which is transformed to NO. (Due to the low temperatures in a fluidized bed plant, 10 to 30 % only of the fuel-nitrogen and no nitrogen from the air is converted to NO.) A lack of O2 favours rather the competing reaction which yields molecular N2. The dependencies of SO and NO emissions are mostly active in opposite directions (figure 2). A good insigit into tze conditions leading to NO formation is possible with the secondary air reactor. When plotting the NOx emission against different incremental primary airlsecondary air ratios, a NO mmimum is met at a distribution of primary versus secondary air of 50 : 50. This &fect was most obvious in reactor no. 1 (4), whereas it was less pronounced in the bigger reactor no. 111 where, at the same time, the maximum emission values were reduced. The lowest values were abserved in the semi-technical reactor (figure 8); they were in the same order of magnitude which prevails also in other larger plants. From this may be concluded that the NO emissions measured in the laboratory reactors are atypically high. The formation of coarse bubbles in big reactors bring about a certain distribution of O2 as high as into the upper bed zones. Such by-pass effect can be compared with the feed of secondary air. Consequently, the way how oxygen acts on the coal and, possibly, the removal of reducing volatile coal components are main determinants for NO emission. Emissions from the semi-technical plant may be considered typicalXfor NO emissions from full-scale plants (figure 8), with 1 g NOZ/kWh being approxizately equivalent to 200 ppm NO. So, even though the numerical values obtained from laboratory measurements are exaggerated in respect of their absolute value and do not allow any generalization as to NOx emissions, one may nonetheless derive certain tendencies (e.g. dependence on excess air) which can be scaled-up to bigger plants. Typical figures for SO emissions cannot be identified since the main influential 2 factor on SO emission will be the amount of limestone added. SO emission, there- 2 fore, is only to a small extent typical for a given plant. Fi re 3 shows a dependence on the limestone/sulphur mole ratio when feeding di erent coals high in ash and with varying sulphur contents, but adding one same limestone at pressures of 1.1 and 4.5 bar. It is the spontaneous desulphurization of coals rather than their sulphur content which brings about the difference in SO emissions, -- emissions which on a laboratory scsle can be reduced to zero. To And out the limestone with optimum sulphur capturing efficiency (i .e. accomplishing the desired desulphurization with admixture of the possible minimum sorbent amount), some three dozens of limestomes of different geological formations, deposits, and trade marks were tested (5). Geologically young and porous limestones appear to be best suited. 221
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Diminishing C-loss along with pressure rise is rel<strong>at</strong>ed to an increased 0<br />
tr<strong>at</strong>ion , whereas diminishing C-loss along with rising temper<strong>at</strong>ure is <strong>at</strong>tr?b%?:i<br />
higher reaction velocity. Increasing fluidizing velocities reduce <strong>the</strong> residence time<br />
<strong>of</strong> <strong>the</strong> <strong>coal</strong> in <strong>the</strong> reactor and, thus, cause higher C-losses. If one found a means<br />
<strong>of</strong> extending this residence time -- be it by appropri<strong>at</strong>e plant design or/and b <strong>coal</strong><br />
prepar<strong>at</strong>ion -- <strong>the</strong> specific he<strong>at</strong> release r<strong>at</strong>e could be improved proportion<strong>at</strong>e& to<br />
<strong>the</strong> fluidizing velocity.<br />
A longer residence time <strong>of</strong> <strong>the</strong> <strong>coal</strong> by means <strong>of</strong> increased bed height will diminish<br />
C-losses , too.<br />
C-loss may be influenced also by <strong>coal</strong> prepar<strong>at</strong>ion measures. As shown on figure 3,<br />
<strong>the</strong> C-loss will, when fueling closely sized <strong>coal</strong> fractions, pass through a maximum<br />
as soon as <strong>the</strong> particle diameter approches <strong>the</strong> elutri<strong>at</strong>ion cut point. Coarse <strong>coal</strong><br />
grains will remain in <strong>the</strong> bed up to <strong>the</strong> moment where <strong>the</strong>y are burnt down to a<br />
size allowing <strong>the</strong>ir elutriution or preventing <strong>the</strong>m from being recycled by <strong>the</strong><br />
inertial separ<strong>at</strong>ors. With sufficiently small fractions (<strong>coal</strong> dust) <strong>the</strong> reaction time<br />
is apparently shorter than <strong>the</strong> residence time in <strong>the</strong> reactor space so th<strong>at</strong> <strong>the</strong> <strong>coal</strong><br />
particles are almost completely burnt up. As far as industrial plants are concerned,<br />
<strong>the</strong> logical conclusion from this is to separ<strong>at</strong>e <strong>coal</strong> dust &om <strong>the</strong> coarser fractions<br />
and blow <strong>the</strong> dust pneum<strong>at</strong>ically into <strong>the</strong> fluidized bed from below, in order to allow<br />
a maximum residence time <strong>of</strong> <strong>the</strong> dust and avoid erosion in <strong>the</strong> feed ducts, whereas<br />
<strong>the</strong> coarse fractions, being introduced from above, are allowed sufficient time to<br />
spread over <strong>the</strong> bed while being burnt up. In this case it can be taken from <strong>the</strong><br />
diagrams, e.g. figure 3, where <strong>the</strong> prepar<strong>at</strong>ion cut points for each specific plant<br />
are viz . which granular fraction should be separ<strong>at</strong>ed and lor fur<strong>the</strong>r comminuted.<br />
Examin<strong>at</strong>ion <strong>of</strong> <strong>the</strong> carbon carry-over by means <strong>of</strong> screening for its size distribution<br />
does not yield accur<strong>at</strong>e results since char aggreg<strong>at</strong>ions will disintegr<strong>at</strong>e. The results<br />
<strong>of</strong> figure 3 are, however, reconfirmed by this approxim<strong>at</strong>ive evalu<strong>at</strong>ion. Moreover it<br />
can be verified from fly ash separ<strong>at</strong>ion in two subsequent cyclones th<strong>at</strong> <strong>the</strong> fine dust<br />
from <strong>the</strong> second cyclone is very low in carbon, whereas <strong>the</strong> "coarse dust" <strong>of</strong> <strong>the</strong><br />
first one will always contain <strong>the</strong> bulk <strong>of</strong> <strong>the</strong> unburnt carbon.<br />
Apart from <strong>the</strong> determinable and adjustable oper<strong>at</strong>ional parameters, C-loss is also a<br />
function <strong>of</strong> <strong>the</strong> specific plant parameters. Measuring d<strong>at</strong>a can best be reproduced in<br />
labor<strong>at</strong>ory equipment. When doing so, one observes o<strong>the</strong>r and so far not measurable<br />
oper<strong>at</strong>ional conditions which bear on <strong>the</strong> results. Among <strong>the</strong>se have to be considered<br />
<strong>the</strong> size distribution <strong>of</strong> <strong>the</strong> fluidized bed ash particles which changes during opera-<br />
tion, or changing fluidity and cohesive <strong>properties</strong> <strong>of</strong> <strong>the</strong> bed ash when adding<br />
various grad<strong>at</strong>ions <strong>of</strong> limestone.<br />
A comparison <strong>of</strong> <strong>the</strong> C-loss measured in reactor no. 1 with th<strong>at</strong> <strong>of</strong> <strong>the</strong> semi-technical<br />
Plant V (figure 5) -- <strong>the</strong> cross-section <strong>of</strong> <strong>the</strong> free-board has been enlarged in both<br />
units -- shows good coincidence. It should be borne in mind, however, th<strong>at</strong> here<br />
varying particle grad<strong>at</strong>ions and bed heights compens<strong>at</strong>e each o<strong>the</strong>r in a way not<br />
clearly identified so far.<br />
As was expected, <strong>the</strong>re are differences also in <strong>the</strong> C-losses for <strong>the</strong> different<br />
labor<strong>at</strong>ory reactor types since inertial separ<strong>at</strong>ors are not optimized. This is not<br />
disturbing as long as feed m<strong>at</strong>erials, viz. types <strong>of</strong> limestone and <strong>coal</strong>, are<br />
compared by measurements in one reactor only. As soon as it comes to scaling up<br />
results, however, one has to know about <strong>the</strong> reasons and influences <strong>of</strong> specific<br />
oper<strong>at</strong>ional conditions.<br />
220