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    Slaking of lime

    Johan B. HolmbergDepartment of Chemical Engineering II, Lund Institute of Technology,P. O. Box 124, S-221 00 Lund, Sweden

    Quicklime is produced when limestone is heated above 900 C, a temperature at which

    limestone decomposes to carbon dioxid and quicklime (CaO). Quicklime exists in manydifferent qualities. Limes of different quality have been characterised, wet slaked and dry

    slaked. The characterisation in combination with the wet slaking suggested that therelationship between the surface concentration of calcium and carbon was the best measure

    for the lime reactivity in the slaking process. The higher value for the relationship the morereactive was the lime. The wet slaking tests showed that the differences in reactivitydecreases when temperature is raised or calcium chloride is added to the water. The dry

    slaking tests showed upon very small differences considering the slaking degrees for

    different conditions and different qualities of lime. However the tests showed on arelationship between water content in the reactor and the specific surface for the product,the higher quote the higher specific surface.

    Introduction

    Quicklime is produced by heatinglimestone above 900 C, a temperature at

    which limestone decomposes to carbondioxid and quicklime (CaO). The productquality is among other things dependent on

    this calcining process. Prolonged heatingor heating at too high temperatures

    generate a less reactive lime. Anotherproblem is how the calcining process isperformed, what sort of furnace that is

    used. Besides how the calcining process isdone, is the product quality governed by

    the amount of impurities in the lime.Quicklime is often used in many

    processes involving slaking, it is therefor

    of utmost importance knowing whether the

    quicklime will be slaked or not in theslaking process. To test this quicklimes ofdifferent qualities were investigated. Thelimes tested were a couple of Chinese

    limes, a Swedish lime and a lime fromPoland.

    Characterisation of quicklime

    The normal measurements whenquicklime is characterised are the amount

    of free lime and total lime in the product,

    the porosity of the lime, the amount ofimpurities and the particle size distribution.

    Only three different limes were fully testedand characterised. Six additional Chineselimes were tested for impurities, the lime

    content and reactivity. The three limes thatwere fully tested were they from Poland,

    Sweden, a lime from Partek Nordsjkalk,and one from China

    The tests for available lime showed on a

    distinct difference between the limes.

    Table 1 Content available lime

    Type of lime Available content (%)Swedish 91Chinese 78

    Polish 66

    To test the porosity a whole varity ofvariables were tested since it was notpossible to measure the porosity directly.

    The measurement made were the specificsurface, the pore size distribution, the pore

    volumes and the density.

    Table 2 Specific surface (BET)

    Type of lime BET-surface (m2/g)Swedish 1.15Chinese 2.67

    Polish 1.10

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    Table 3 Average pore size (BJH)

    Type of lime Pore diameter ()Swedish 144Chinese 200Polish 182

    Table 4 Pore volumes (BJH)

    Type of lime Pore volume (cm3/g)Swedish 0.0035Chinese 0.0118

    Polish 0.0044

    Table 5 Density

    Type of lime Density (kg/m3

    )Swedish 1210

    Chinese 1250Polish 1300

    Since quicklime belongs to the bulkchemicals it is difficult to measure the

    density. The density is therefor given asthe figure for the weight per volume when

    the lime no longer could be compressedthrough shaking.

    The figures listed gave no real answersto how reactive each lime would becompared to the others. The density

    implies that the Swedish lime should bemuch more reactive than both the polish aswell as the Chinese lime. The measured

    specific surface and the measured porevolumes indicate that the Chinese lime

    should be much more reactive than boththe Swedish and the Polish lime, whichshould show almost the same reactivity.

    The average pore size for the different limegave no new light to which lime that is the

    most reactive.

    Table 6 Particle size distribution

    Swedish Chinese Polish

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    temperature rise was measured and thiswas correlated to the conversion. The

    slaking procedure was carried outaccording to the ASTM-standard C110.Besides that, the initial temperature

    dependence was tested.

    The Swedish lime at different

    starttemperatures

    0

    10

    20

    30

    40

    50

    0 5 10

    Time (min)

    Tempdiff(C

    25 degreas

    30 degreas

    35 degreas

    40 degreas

    50 degreas

    The Polish lime at different

    starttemperatures

    0

    5

    10

    15

    20

    25

    30

    0 10 20 30

    Time (min)

    Tempdiff(C

    25 degreas

    30 degreas

    35 degreas

    40 degreas

    50 degreas

    The Chineese lime at different

    starttemperatures

    0

    10

    20

    30

    40

    0 5 10Time (min)

    Tempdiff(C

    25 degreas

    30 degreas

    35 degreas

    40 degreas

    50 degreas

    Figure 1 Different limes at different starttemperatures

    In the figure above we can see bigdifferences in slaking times for the Polishlime to the others and we can also notice

    that the Chinese lime is a little morereactive than the Swedish lime. We canalso notice the slaking time seems to

    converge with raised start temperature forthe slaking. Parts of the fact that the Polish

    curve increases its reactivity depends onthe fact that the time difference betweentotal slaking time and the slaking time

    according to the ASTM-standard levels outwith raised start temperature.

    Another way of raising reactivity is byadding calcium chloride.

    Table 8 Slaking with addition of CaCl2additive none CaCl2

    Type of lime Time (min) Time (min)Swedish 6.33 2.67

    Chinese 4.67 2Polish 17 7.67

    The figures in the table above are theslaking times you get if you add 10 grams

    of calciumchloride per litres of water. Thefigures clearly show that the slaking timesdecreases fairly when you add

    calciumchloride.

    Figure 2 The Polish lime wet slaked with calcium

    chloride

    Whats interesting in the graph above is

    that there is a minimum slaking time whencalcium chloride is added and that the lessreactive the lime is the more effect has

    increasing the dose of calcium chloride.

    Limes slaked differently

    0

    20

    40

    60

    0 20 40Time (min)

    Tempdiff(C)

    Polish lime

    Polish lime

    plus 20 g

    CaCl2x2H2O

    Swedish lime

    Polish lime

    50 C

    Figure 3 The Polish lime compared to the Swedish

    Polish lime with different ammonts of

    calciumchloride added

    0

    10

    20

    30

    40

    0 10 20 30

    Time (min)

    Tempdiff(C) 0 g/ l

    4 g/ l

    10 g/ l

    20 g/ l

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    What you can see in the last figure isthat when both raising the start temperature

    and adding calcium chloride to the slakingwater the difference in slaking timesbetween the Swedish lime and the Polish

    lime decreases dramatically.As with many positive effects there is

    also a downside. Adding calcium chloridelowers the BET-surface of the slakedproduct, see Table 9.

    Table 9 BET-surfaces

    Additive none CaCl2Sort of lime Surface

    (m2/g)Surface(m2/g)

    Swedish 26.5

    Chinese 23.4 9.7Polish 18.2 7.9

    The surfaces in the table above are those

    for the products slaked at a startingtemperature of 25 C.

    The third way of raising the limesreactivity is grinding. The Polish lime was

    ground, the fraction above 125 m was

    ground to under 125 m, when you

    compare this reactivity to that one for theoriginal lime you notice that reactivity has

    increased dramatically, as you can see inthe figure below

    Polish lime ground

    010

    20

    30

    40

    0 10 20 30

    Time (min)

    Tempdiff(C)

    Polish lime

    Polish lime

    ground

    Figure 3 The Polish lime ground

    The six additional samples from Chinawere also slaked. These samples were

    slaked with another equipment totallyaccording to the ASTM-standard. Since

    these latter samples were slaked with thesame equipment and at the same time they

    were fully comparable. Besides one of thesamples all samples had a well definable

    slaking time according to the ASTM-standard. However one of the sampleslacked this cause there were no

    temperature measurement made in the endbesides the end point. Plotting the slaking

    times against the ratio between calciumand carbon atomic surface concentrationsgave an almost perfect linear function apart

    from the outlier discussed earlier.

    The slaking time versus the

    relationship between calcium and

    carbon on the surface

    0

    5

    10

    1520

    25

    0 0.2 0.4 0.6 0.8 1

    Ca/C (atomic concentrations)

    Slakingti

    me

    (min)

    Figure 4 The slaking time plotted against surface

    concentrations of calcium and carbon

    The slaking seems to be divided into twoparts one initial part that probably involves

    bursting of the particles and a second phasethat seems to be a part where the reaction

    goes on, on the surface of the cores of theparticles. The data from the wet slakingwere fitted to the shrinking core model for

    a surface reaction.

    Shrinking core reaction control for the

    Swedish lime

    0

    0,2

    0,4

    0,6

    0,8

    0 100 200 300

    Time (s)

    1-(1-x)^1/3

    25 degreas

    30 degreas

    35 degreas

    40 degreas

    50 degreas

    Figure 5 Shrinking core reaction control for the Swedish

    lime

    The model was valid for conversions

    between 0.4 and 0.9. The figures wereadjusted for the different temperatures and

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    the temperature dependence was calculatedaccording to the arrenhius equation and

    gave the activation energies for the slakingprocesses, 38 kJ/mol for the Swedish lime,56 kJ/mol for the Polish and 60 kJ/mol for

    the Chinese lime.

    Dry slaking

    The limes from Sweden and Poland

    were also slaked in a two-step dry slaker.The slaker could be modelled as a tank

    followed by a tube. What was measuredwas the specific-surface and slakingdegrees of the slaked products. The slaking

    degrees were measured with a TGA, where

    the slaking degrees could be calculatedfrom the weight loss when the lime washeated above 600 C, a temperature atwhich lime decomposes into quicklime and

    water.It was showed that the slaking degrees

    for the Polish lime were close to those forthe Swedish lime. The slaking degrees are

    correlated to the content available lime.

    Polish lime

    0

    5

    10

    15

    20

    25

    30

    0 0,2 0,4 0,6 0,8

    Relationship lime/water (kg/kg)

    BET-surface(m2/g)

    5.85 kg/h

    4.12 kg/h

    5.2 kg/h

    Figure 6 The specific surface plotted against the water

    dosation

    In the figure above you can clearly seehow the specific surface of the slaked

    product depends on the water content inreactor. This result was not dependent ofthe lime quality.

    Slaking with addition of Triethanolaminwas tested for the Swdeish lime. The major

    difference was that BET-surface doubledand that the amount of small pores in theproduct increased.

    Results and disscussion

    It was showed that the only really goodway of measure and characterise lime is by

    measuring the relationship between

    calcium and carbon on the surfaces. Thecorrelation between the reactivity and thedifferent surface concentrations maydepend on some sort of mass transport

    problem associated with the amount ofcarbon on the surfaces or it may somehow

    be connected to the fact that there is muchcarbonates in the lime.

    It has further been shown that the wet

    slaking times for different limes can bedecreased by raising the temperature or by

    adding calcium chloride or by doing both.This temperature dependence behaviourmay explain why there is only small

    differences between slaking degrees in thedry slaking.

    Its also suggested that the differences inspecific surfaces in the dry slakingexperiments arise from the fact that the

    temperature is lowered when extra water isadded and that this might have an positive

    influence on the specific surface.

    Literature cited

    ASTM C 110-87 (1987) Standard Test M ethods frPhysical Testing of Quick lime, H ydrated L ime andL imestone

    Babatschev, G.,Kassabova, M. (1969) E influss vonTemperatur und E lek trolyten auf die H ydration von

    ungelschtem Kalk, Zement-Kalk-Gips (22)312-316

    Becker, H., Zander, Von H. (1976) Uber dieN eutralisationsgeschwindigkeit von nass oder trock en

    Swedish lime

    0

    10

    20

    30

    40

    0 0,2 0,4 0,6 0,8Relationship lime/water

    (kg/kg)

    BET-surface(m2/

    g)

    5.2 kg/h

    6.7 kg/h

    7.8 kg/h

    3.7 kg/h

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    gelschten Kalk hydraten in A bhngigk eit von derenH erstellungsbedingungen, Zement-Kalk-Gips (29)381-387

    Becker, H., Zander. Von H. (1977) Uber dieL sungsgeschwindigk eit von Kalk hydraten, Zement-

    Kalk-Gips (30) 287-292Boynton, R. S. (1966) Chemistry and technology of

    lime and limestone, 1:a upplagan, John Wiley &Sons

    Campbell, I. M. (1988) Catalysis at surfaces, 1:aupplagan, Chapman and Hall

    Devismes, von R., Foster, P., Perraud, R. (1990)E ntschwefelung von schwefeldioxidreichen rauchgasenmit branntkalk und kalk hydrat, Zement-Kalk-Gips (43) 38-42

    Frank, G., Achenbach, G. (1987) E influss vonChlorid-Ionen auf das L schen von Kalk, Zement-Kalk-Gips International (40) 479-482

    Frank, G. (1977) E influss der L schbedingungen aufdie Qualitt des gebildeten Calciumhydroxids beim

    N asslschen von Kalk, Zement-Kalk-Gips (30)34-39

    Giles, D. E., Ritchie, I. M., Bing-An, X. (1993)The k inetics of dissolution of slaked lime,Hydrometallurgy (32) 119-128

    Schmitz, F., Hennecke, H. P., Bestek, H.,

    Roeder, A. (1984) Trock engelschtes Kalk hydratmit grosser Oberflche-E in wirk sames reagenz zur

    bindung saurer abgasbestandteile Teil1: Herstellung

    im labormastab und ausblick ber die verwendungbei der rauchgasreinigung, Zement-Kalk-GipsInternational (37) 530-533

    Hennecke, H. P., Kning, W., Roeder, A.,Schmitz, F., Stumpf, T. (1986) Trock engelschtesKalk hydrat mit grosser Oberflche-E in wirk sames

    reagenz zur bindung saurer abgasbestandteile Teil2: A ufbau und betrieb der k leinproduktionsanlage;

    betriebsergebnisse aus versuchen z ur trock ensorptionvon schadstoffen aus unterschiedlichen abgasen,Zement-Kalk-Gips International (39) 251-258

    Ingesson, E (2000)H ydrox id OH- sock ermetoden

    Johnson, W. A., Mehl, R. F. (1939) Trans AIME(135) 416

    Levenspiel, O. (1972) Chemical reaction engineering,2nd upplagan, Wiley international editions

    Ohnemller, W., Hupe, B. (1969) D ie H ydrationdes Branntk alkes in der Kalk sandstein-Rohmasse

    und ihre Bedetung fr die Steinfestigk eit vor und nachdem Dampfhrten, Zement-Kalk-Gips (22) 116-121

    Ritchie, I. M., Bing-An, X. (1990) The kinetics oflime slak ing, Hydrometallurgy (23) 377-396

    Schlegel, E., Werner, W., Hartmann, H-J. (1976) Z ur H ydrationsgeschwinigk eit von CaO,Silikattechnik (27) 377-378

    Zeilnhofer, J., Ploetz, C. (1998) V ollautomatischeKalk -Trock enlschanlage, Zement-Kalk-GipsInternational (51) 494-499

    R eceived for review february 5, 2001