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SD Vision - Halyps Cement

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24<br />

Monselice cement plant: electrostatic precipitator for dedusting gases<br />

to the catalytic system for NOx abatement<br />

reaction among these compounds and the<br />

nitrogen oxides to form elementary nitrogen<br />

and water. This method, known as SNCR<br />

(Selective Non-Catalytic Reduction), has<br />

some advantages, including that of being<br />

easily applicable also to existing plants,<br />

especially dry process ones.<br />

However, it also has drawbacks, including<br />

that of releasing ammonia from the stack<br />

(ammonia slip) when, with the intent to<br />

minimize NOx emissions as much as possible,<br />

reagent is added at higher rates than those<br />

required by the reaction stoichiometry.<br />

The simultaneous adoption of the abovedescribed<br />

techniques allows cutting the<br />

emissions from a cement kiln to 500 mg/<br />

Nm 3 dry at 10% oxygen. Other industries<br />

and the energy sector in particular have<br />

been using another “secondary method”<br />

for some time, namely the injection of<br />

aqueous ammonia solution into the gas<br />

stream at temperatures of around 350°C. In<br />

this case, the reaction can take place only in<br />

the presence of a catalyst, hence the name<br />

of the method known as SCR (Selective<br />

Catalytic Reduction). The catalyst consists<br />

essentially of vanadium and titanium<br />

oxides, mixed in appropriate proportions<br />

and so arranged as to obtain hollow bricks<br />

that maximize the surface/volume ratio<br />

while minimizing the amount of catalyst<br />

per volume unit of treated gas. In a cement<br />

kiln, the temperature of gases exiting the<br />

preheater is between 300°C and 350°C:<br />

so, extending sic et simpliciter this kind<br />

of technique to cement kilns would seem<br />

feasible. For some time, attempts in this<br />

direction have been made with unsuccessful<br />

results, not so much in terms of reducing<br />

emissions, but rather for the negative effects<br />

on kiln performance, which showed disadvantages<br />

in terms of energy consumption,<br />

steady operating conditions and production<br />

levels. Actually, the amount of dust in the<br />

gases from the preheater is higher than the<br />

amount measured in the hot gas circuit of<br />

a coal boiler. Such a high amount of dust<br />

clogs the narrow channels of the catalyst<br />

requiring continuous cleaning by means<br />

of high-pressure air jet cleaning, resulting<br />

in higher energy consumption. Despite<br />

cleaning, it is impossible to run the plant<br />

correctly because of the frequent stops and<br />

lower production levels.<br />

Italcementi Group also wanted to verify the<br />

real effi cacy of a catalytic system and did it<br />

in a particular context: a Lepol kiln, characterized<br />

by ammonia emissions from the raw<br />

materials of some tens of milligrams per cubic<br />

meter, was equipped with a catalytic system<br />

very similar to the above mentioned ones,<br />

in which, however, nitrogen oxides were<br />

used to abate ammonia. The system has<br />

proved to be very effi cient, also considering<br />

that the dust contained in the gas was only<br />

a few grams per cubic meter, thus demonstrating<br />

that the only real hindrance to a<br />

correct operation of the catalytic system<br />

on a cement kiln is that of reducing the<br />

concentration of dust transported by the<br />

gas to be treated to values compatible<br />

with the catalyst. After being discussed<br />

and analyzed at length, the innovative idea<br />

proposed by the Group Technical Center<br />

was considered valid and fi nally patented.<br />

This consisted in the installation of a technological<br />

electrostatic precipitator between<br />

the preheater’s exhaust gas outlet and the<br />

inlet of the system (catalytic reactor) for<br />

reducing dust to values which are certainly<br />

at least compatible with the best operating<br />

conditions required by the catalyst. The<br />

electrostatic precipitator must work at<br />

medium to high temperatures, as occurs<br />

for similar plants treating emissions from<br />

linker coolers. No specially high effi ciency is<br />

needed since the dust concentration value<br />

required downstream of the electrostatic<br />

precipitator is still of the order of grams per<br />

cubic meter. This solution will be applied to<br />

all the new lines that are being designed for<br />

Italian plants and for which the authorisation<br />

process is in progress. The adoption<br />

of this technique is expected to provide a<br />

continuous NOx emission value of around<br />

200 mg/Nm 3 under standard reference<br />

conditions while ensuring continuity of<br />

operation, equal throughput, reasonable<br />

electricity consumption levels and, last<br />

but not least, optimal preservation of the<br />

catalyst. The emission level associated with<br />

this technique corresponds to the value<br />

specifi ed in the latest BAT document for<br />

the cement industry, which updates the<br />

2001 version. Among the BATs for nitrogen<br />

oxides, the new document also indicates the<br />

SCR technique, which, however, requires<br />

further studies before its fi nal application.<br />

New techniques for SO 2<br />

emissions reduction<br />

Though the problem of sulfur oxide<br />

emission cannot be considered typical of<br />

the cement industry, there are however<br />

cases where the sulfi des present in the<br />

raw materials may generate SO 2 emissions.<br />

In fact, the sulfur added in the process is<br />

oxidized at temperatures that are too low<br />

to make its assimilation possible by reaction<br />

with the alkaline materials present in the<br />

kiln. It is well known, however, that sulfur

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