Patent Application
20180050303
The present invention relates to a method and a device for the treatment of exhaust gases which arise during the production of cement clinker in a rotary kiln.
Cement production by burning raw meal to form clinker requires high temperatures at which the formation of various pollutants, especially of nitrogen oxides, cannot be prevented. In view of the increasingly lower limit values for the emission of pollutants, a variety of methods have been developed to remove them from the exhaust gas. The following proposals show the prior art, particularly with respect to denitrification.
A first approach consists in the conversion of the nitrogen oxides, NO and NO2, collectively referred to as NOx, with ammonia or urea solution, typically at 900 to 1000° C. This method is referred to as selective non-catalytic reduction, or SNCR for short. An example of this is WO 201 2/1 761 6 A1 which describes a method in which ammonia or a compound releasing ammonia, such as urea, is supplied as the reagent to raw meal preheating. In order to improve mixing, exhaust gas is removed from preheating, freed from dust, and then the reagent is added to it. The dedusted gas which is charged with reagent is then returned to the preheater.
More effective denitrification can be achieved with the aid of selective catalytic reduction, SCR for short. Ammonia, optionally produced in situ from compounds releasing it, is also used as the reagent. The reaction is carried out on catalysts which mainly consist of titanium dioxide and are doped with vanadium pentoxide and tungsten trioxide. One example is CN 102698600 A, according to which the exhaust gas from raw meal preheating is at least partially passed through a corresponding catalyst. DE 10 2011 001 773 A1 proposes to also supply the exhaust gases from a predrying of alternative fuels to the same catalyst, such that carbonaceous odorous substances and ammonia contained therein are also reacted on the catalyst.
The fact that an excess of ammonia is necessary for a substantial degree of reaction of the nitrogen oxides is a problem in the SNCR and the SCR. In general, the lower the emission limit value, the higher the excess must be. However, excessively high excess leads to the unreacted ammonia being contained in the exhaust gas after the reduction reaction, so-called ammonia slip, which is only permitted to a limited extent. In order to solve the problem, it is proposed in U.S. Pat. No. 5,510,092 A to purify the exhaust gas substantially by means of SCR and to additionally introduce ammonia in an SNCR zone only when an excessively high NOx concentration in the exhaust gas is detected. This is to ensure safe compliance with very low nitrogen oxide contents in the exhaust gas, without a large excess of ammonia being necessary and being able to enter the exhaust gas.
A further proposal for exhaust gas purification can be found in DE 10 2011 001 933 A1. The use of SCR in the exhaust gas of raw meal preheating is recommended for denitrification. In addition, exhaust gas from the raw material mill, in which the raw materials are ground into raw meal, is to be treated with alkali hydrogen carbonate and/or alkali carbonate in order to remove acidic pollutants such as sulphur oxides, hydrogen chloride and hydrogen fluoride. Thereby a reduction of the mercury content should also be achieved.
US 2009/0252665 A1 describes a combination of catalytic or non-catalytic reduction of the nitrogen oxides with a subsequent catalytic decomposition of excess ammonia for the purification of exhaust gas from steam boilers, heating units, kilns and other devices generating exhaust gas. There are no indications as to how this method could be used in cement production.
However, further requirements arise in cement production in addition to denitrification. The exhaust gas from preheating is generally guided into the raw material mill; first dust removal takes place in the exhaust gas flow from the mill at a filter upstream of the exhaust gas outlet. In order to protect the mill and this main exhaust gas filter, the exhaust gas must be de-acidified depending on the composition of the raw materials and the fuel material, which usually takes place during gas purification by supplying calcium hydroxide. Sulphur oxides and other acid gases are thus effectively removed from the exhaust gas. If acidic exhaust gases are allowed to enter the main filter, extensive corrosion may result, in particular in the clean gas area.
A further, specific problem is that, during preheating of the raw meal in the heat exchanger, ammonia contained in the raw material is also released. As a rule, ammonia from the SNCR and ammonia related to the raw material are adsorbed to the raw meal in the raw material mill. Ammonia is then accumulated in the system between the preheater and raw material mill and raw meal silo. The raw material mill is operated on average only about 85% of the time the rotary kiln works. During the time period in which the mill is not operated, so-called direct operation, the exhaust gas from the preheater directly enters the main filter. As a result, ammonia is increasingly drawn into the exhaust gas, since this is no longer adsorbed on the raw meal in the mill. During the period of direct operation, the previously deposited and accumulated ammonia is additionally released and temporally limited but high ammonia emissions result. The percentage of direct operation can be up to 30% or even just 5% of the kiln operating time in individual cases.
The object of purifying exhaust gases from cement production, in which the increasingly lower limit values can be fulfilled and the costs and the energy requirements remain acceptable, is therefore still not completely solved.
Surprisingly, it has now been found that very efficient exhaust gas purification can be achieved in cement production by carrying out denitrification by means of SNCR with a sufficiently high excess of reagent and subjecting the exhaust gases from preheating to a combined gas conditioning and catalytic oxidation.
The above object is therefore solved by a method for the purification of exhaust gas from the production of cement in a rotary kiln, in which raw materials are ground in a mill to form raw meal, raw meal is preheated in countercurrent in a preheater with exhaust gas from the rotary kiln and optionally precalcined, preheated and optionally precalcined raw meal is supplied to the rotary kiln and burned in the rotary kiln to form cement clinker, the exhaust gas from the rotary kiln is denitrified before entry into the preheater of a selective non-catalytic reduction with a reagent which provides ammonia and wherein, according to the invention, the exhaust gas from the preheater is subjected to gas conditioning and catalytic oxidation. The object is further solved by a device for gas conditioning and catalytic oxidation which is arranged between mill and preheater according to the invention in a plant for the production of cement clinker, comprising a mill, in which raw materials are ground to form raw meal, a preheater, in which the raw meal is preheated in countercurrent with exhaust gas from a rotary kiln and optionally precalcined, the rotary kiln, in which the preheated and optionally precalcined raw meal is burned to form cement clinker, and a section between the rotary kiln and preheater, in which nitrogen oxides are reduced with a reagent which provides ammonia. Gas conditioning can advantageously comprise gas purification with alkaline substances, preferably calcium hydroxide.
The plant for cement production largely corresponds to the known plants, therefore the known parts are not described in detail here. A detailed description can be found, for example, in W. H. Duda; Internationale Verfahrenstechniken der Zement Industrie, Volumes 1 to 3, 1985, Bauverlag Wiesbaden and Berlin.
According to the invention, a known SNCR is provided on the one hand. This is placed between the rotary kiln and preheater to comply with the desired reaction temperature of 830° C. to 970° C. By means of the SNCR, nitrogen oxides which have been formed in the rotary kiln or during the combustion of fuels or which originate from the raw material are reduced to nitrogen by adding ammonia or a compound which releases ammonia as a reagent. Ammonia or urea is preferably used as a reagent, in particular as an aqueous solution. The ratio of reagent to nitrogen oxides and the feed point are selected in such a way that the nitrogen oxides are reacted as completely as possible. For example, molar ratios for reagent, calculated as ammonia to nitrogen oxides (NH3: NOx) of 1.1 to 2.5, preferably 1.3 to 1.6, are suitable. According to the invention, less consideration has to be given to a possible ammonia slip than in the prior art. This makes it possible to achieve an extensive conversion without the need for an SCR catalyst, which limits plant costs. Nitrogen oxide contents in the exhaust gas of <200 mg/m3 and even 150 mg/m3 are regularly achieved.
The SNCR takes place at a location in the plant where the exhaust gases are at a suitable temperature, for example from 800 to 1000° C., preferably from 830 to 950° C. As a result, no additional energy is required for the SNCR and the amount of ammonia, which would otherwise be ineffective for reduction and possibly burns itself to form NOx, is kept low.
According to the invention, selective catalytic oxidation (SCO) and gas conditioning (GK) take place between the preheater and the mill in addition. For direct operation, the branch for the bypass of the mill is located after the gas conditioning with catalytic oxidation such that only exhaust gas which has been treated according to the invention with both SNCR and with SCO and GK is supplied to the main exhaust gas filter.
Catalytic oxidation serves to oxidise ammonia related to the SNCR and the raw material in the exhaust gas to form nitrogen. Suitable catalysts are known to the person skilled in the art; they are used, for example, in exhaust gas treatment in fertiliser production. The catalysts used for the SCRs based on titanium dioxide catalyst carriers doped with vanadium pentoxide or tungsten trioxide can also be used, but it is preferred to increase the activity by adding precious metals such as palladium, rhodium and platinum, as well as copper or magnesium. The optimum temperature of the exhaust gases during oxidation is in the range from 275 to 380° C.
The catalysts advantageously also oxidise further existing pollutants. Therefore, mercury, which is difficult to remove from the exhaust gas in the elementary form, is oxidised and can thus be separated more effectively in the main filter. Sulphur dioxide is oxidised to form sulphur trioxide, which can be bound much more easily than SO2 by means of dry sorption or semi-dry sorption. As mentioned above, the purifying effect with regard to sulphur oxides can be further optimised by means of gas purification with alkaline substances. Furthermore, volatile medium to long-chain hydrocarbons, so-called volatile organic compounds (VOC), are oxidised to form H2O and CO2.
Gas conditioning of the exhaust gas is primarily required to adjust the temperature and gas humidity of the exhaust gas to the respective optimum range for downstream dust separation devices such as, for example, bag filters or electric separators. This can have a positive influence on the dust and gas properties and thus reduce the installation and operating costs of dust removers.
According to the invention, catalytic oxidation and gas conditioning are carried out on an exhaust gas containing dust. In the prior art, previous partial dust removal is deemed necessary for a successful SCR. This is not necessary according to the invention. However, it is preferred to blow the catalyst clear with compressed air from time to time. For this purpose, a rotating unit with offset nozzles varying in cross section is preferably used. The pressure can be down to 0.8 bar at high compressed air flow rates, and up to 6 bar, maximum 8 bar at low compressed air flow rates. The rotating unit can be driven by the compressed air, or mechanically by a bevel gear drive. The bearing is expediently made of ceramic material, preferably of silicon carbide, and air purged. A hard metal bearing is also possible. In any case, the bearing should be free of lubricant which is decomposed to be non-lubricating at the high application temperature.
It is also advantageous to preheat the compressed air to at least 150° C., preferably to 170 to 275° C., but a maximum of 300° C. As a result, deposits can be prevented which otherwise form on the active surface through shock cooling and the chemical reactions of the gas components taking place at the same time.
In a particularly preferred embodiment, the compressed air is preheated in a heat exchanger by the exhaust gases. Depending on the exhaust gas temperature, the heat exchanger is arranged before or after the oxidation catalyst, but in any case before the gas conditioning stage. If the exhaust gas temperature is over 350° C., the heat exchange is preferably carried out before the catalyst, if it is below 330° C., the heat exchange is preferably carried out after of catalytic oxidation.
The flow rate of the exhaust gas upstream of the oxidation catalyst is expediently in the range from 2.5 to 4.5 m/s, within the catalyst from 4 to 9 m/s. For flow rates near the upper limits, a hardened surface is recommended at the inlet, e.g. over a length of 40 mm. Otherwise the mentioned speed ranges lead to operation which is only slightly abrasive.
To avoid condensation of water and the resulting permanent deposits, a bypass of the catalyst is helpful at the start of operation. The volume flow is typically less than 20% of the normal operating volume flow here. It is further preferred to heat the oxidation catalyst to >140° C. during standstill times. This can preferably be carried out by means of an air circulation heating system for standstill times.
It is particularly preferred to arrange the gas conditioning and catalytic oxidation in a common housing. The combined device is dimensioned as a function of the required gas flow volume and the conditions. Practical diameters of 4 to 9 m allow gas phase currents of up to 400,000 m3/h (standard condition).
The combined gas conditioning and catalytic oxidation preferably comprises the following components in the flow direction of the gas:
a gas inlet region, preferably with a compensating distributor
if necessary, the rotating unit for compressed air cleaning of the catalyst
the catalyst
a gas conditioning section.
A heat exchanger for preheating the compressed air is optionally arranged before the rotating unit or after the catalyst for compressed air cleaning. A dust removal device can be provided at the gas outlet.
The catalyst generally consists of individual cartridges in which the catalyst elements are combined. Expediently, the cartridges have the form of equilateral triangles having cartridge side lengths adapted to the radius of the housing. The individual catalyst elements ideally also have shapes with an equilateral triangular base surface. As a result and through the use of catalyst cartridges arranged in a circle, dust deposit surfaces are minimised. The typical dimensions of the individual catalyst elements are 150 mm side edge length and 500 to 1300 mm element length. These individual catalyst elements can thus be produced with conventional catalyst production matrices. The catalyst cartridges accommodating the individual elements allow variable side lengths, for example 1450 mm. Such a measurement enables a cartridge consisting of 81 individual elements with a catalyst volume per cartridge of 1.2 m3.
Gas conditioning is usually carried out by supplying conditioning water, which is generally injected into the exhaust gas into a so-called evaporative cooler. In this conventional method step, the gas humidity and temperature are adjusted. The preferred gas purification is carried out by adding slurried calcium hydroxide. The dispersion of the absorption solution into the gas to be purified is advantageously achieved by means of a dual-substance nozzle supplied with compressed air. The absorption solution is added mixed together with the normal and cooling conditioning water, which also means that the cooling water balance is not changed and the necessary gas humidity and temperature are also adequately adjusted.
The heat exchanger for preheating the compressed air for cleaning the catalyst is present in the gas flow before or after the catalyst level. Here, the initially cold compressed air is guided through tubes arranged in a serpentine manner and thus increases in temperature. The dust deposited on the tubes is removed at periodic intervals by means of knocking or vibration. The coiled tube is made to vibrate for dust removal. The amplitude is only a few millimetres. This amplitude is nevertheless sufficient to mobilise the necessary shearing forces which exceed the cohesive and adhesive forces of the dust cake and then remove this in the gas direction as a result. In order to ensure natural resonance and the associated vibration of the tubes, a minimum coiled tube length must not be fallen below. Furthermore, the coiled tubes are to be suspended freely. The non-damping coiled tube single path length is usually between 4 and 12m, depending on the arrangement. The tubes used typically have a diameter of 75 to 150 mm for a wall thickness of 4 to 8 mm.
According to the invention, a particular preliminary dust removal is preferably not carried out and the dust concentration according to the preheat exchanger cyclones can also be 100 g/m3 (standard condition) within the normal framework. Known dust separation devices, for example bag filters, are used for the final dust removal of the purified and conditioned exhaust gases after the reactor and the mill. Electrical dust separation devices can also be used.
The invention will be illustrated further with reference to the accompanying figures, without restricting the scope to the specific embodiments described. The invention further includes all combinations of described and especially of preferred featurest that do not exclude each other.
The words “about” or “approx.” in combination with a numerical figure mean that values that are higher or lower by 10% or values that are higher or lower by 5% and in any case values that are higher or lower by 1% are included. If not otherwise specified any amount in % is by weight and in the case of doubt referring to the total weight of the mixture.
Here are shown:
The exhaust gas leaving the housing 9 is largely freed of pollutants. The nitrogen oxides were removed in the SNCR, ammonia and optionally sulphur oxides were converted to nitrogen and CaSO3/4 or removed in the SCO and gas conditioning. Other oxidisable pollutants such as, for example, mercury were transferred into a form which is more easily separable in the filter 3 or converted into harmless substances by oxidation.
| Number | Date | Country | Kind |
|---|---|---|---|
| 15001227.6 | Apr 2015 | EP | regional |
| Filing Document | Filing Date | Country | Kind |
|---|---|---|---|
| PCT/EP2016/000585 | 4/8/2016 | WO | 00 |
