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08 Vosteen_E_Umbruch - Vosteen Consulting GmbH

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Thermal conductivity in W/(m 2 K)<br />

5<br />

4.5<br />

4<br />

3.5<br />

3<br />

2.5<br />

2<br />

1.5<br />

1<br />

0.5<br />

0<br />

Assumed<br />

conductivity<br />

of frozen slag<br />

0 0.5 1 1.5 2 2.5 3 3.5 4 4.5 5<br />

Density in g/cm 3<br />

Density of<br />

frozen slag<br />

Figure 10. Thermal conductivities of heavy and light<br />

refractory bricks at 700 … 800 °C and of air<br />

at 750 °C.<br />

Figure 12 shows the axial profile sslag+brick<br />

(x) as sum of both slag thickness and brick<br />

thickness, the so-called “equivalent brick<br />

thickness”.<br />

The thermographically obtained profiles of<br />

the “equivalent brick thickness” do agree<br />

very well – after primary adaptation of the<br />

(mean) air gap width – with those profiles,<br />

measured directly by drilling.<br />

Drilling must only be done from time to time,<br />

when a kiln has to be cooled down for other<br />

plant-maintenance reasons. Experience has<br />

shown that the air gap width may vary from<br />

kiln to kiln, but doesn’t change much at the<br />

same kiln during its brick life, with the exception<br />

of the first months of operation (brick<br />

settling).<br />

Melting Behaviour of Ashes and Slags<br />

Within the scope of this paper it is not possible<br />

to describe the melting behaviour of<br />

coal ashes (approximately 450 data sets) and<br />

hazardous waste slags (approximately 40 data<br />

sets) in full detail. An extensive report will<br />

be given later in a separate publication. Only<br />

some reference can be made:<br />

As mentioned above, low melting sodiumrich<br />

compounds should be eliminated out of<br />

the solid waste feed as far as possible. Under<br />

high temperature combustion, sodium-halogenides<br />

are rarely found in kiln exit slags,<br />

because they are volatized and transferred –<br />

via evaporation/sulphatation/desublimation –<br />

into the boiler fly ashes. Besides this, the<br />

melting behaviours of coal ashes and hazardous<br />

waste slags are strongly influenced by<br />

— the slag’s iron-content within the slag’s<br />

component-triplet “FeOn – SiO2 – Al2O3”<br />

(well understood as the mass fraction<br />

FeOn / (FeOn + SiO2 + Al2O3), expressed<br />

Total thickness of brick and slag<br />

in mm<br />

in weight-% with<br />

possible values ≥ 0 to<br />

≤ 100 % ) and by<br />

— the “oxidation state”<br />

of the iron oxide FeOn<br />

within the slag’s multicomponent<br />

mixture.<br />

Dissolved Fe2O3 (pure<br />

substance melting<br />

point: 1580 °C) may be<br />

reduced to FeO (pure<br />

substance melting<br />

point: 1390 °C), locally<br />

depending on the<br />

oxidizing or reducing<br />

kiln atmosphere.<br />

The diagrams in Figure<br />

13a (oxidizing conditions)<br />

and Figure 13b<br />

(reducing conditions),<br />

500<br />

400<br />

300<br />

200<br />

100<br />

Thermography of Rotary Kilns<br />

0<br />

0 100 200 300 400 500<br />

Outer shell temperature in °C<br />

VGB PowerTech 9/2002 75<br />

Outer heat transfer coefficient α<br />

W/(m2 K)<br />

70<br />

60<br />

50<br />

40<br />

30<br />

20<br />

10<br />

Total<br />

Thermal radiation<br />

(shell emissivity = 0.95)<br />

Free convection<br />

Figure 11. Outer heat transfer coefficient αoutside (upper<br />

line) by free convection and superimposed<br />

thermal radiation (shell emissivity ε = 0.95).<br />

Equivalent thickness of brick and slag<br />

(thermographical measurement April 28th, 1999)<br />

New brick lining in June 1998<br />

0<br />

0 1 2 3 4 5 6 7 8 9 10 11 12 13<br />

Distance x from kiln entrance in m<br />

Figure 12. Axial profile of the equivalent brick thickness sslag+brick (x) at KILN B, automatically<br />

calculated by „RotaVos“ on April, 28, 1999.<br />

HMP Melting point in °C<br />

under oxidizing conditions<br />

1600<br />

1500<br />

1400<br />

1300<br />

1200<br />

1100<br />

1000<br />

Lignite coal ashes<br />

Hard coal ashes<br />

Hazardous waste slags<br />

0<br />

0 10 20 30 40 50 60 70 80 90 100<br />

Fe 2 O 3 -content within the triplet in weight-%<br />

Figure 13a. Melting-point hammock under oxidizing combustion conditions (half-quantitative<br />

model, based on some 500 data sets, <strong>Vosteen</strong>, 1999).<br />

50<br />

100<br />

CaO-loading of the triplet<br />

in weight-%

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