Granular ICR (intensive Care reactor) denitration agent and preparation method thereof
Technical Field
The invention relates to a technology in the field of environmental protection, provides a domestic garbage incineration ICR denitration process aiming at the problem that the control index of flue gas nitrogen oxides is increasingly strict in the existing domestic garbage incineration process, and discloses a granular ICR denitration agent component and a preparation method thereof, wherein the denitration agent comprises 40-90% of active ammonia component, 5-30% of catalyst component, 1-30% of adhesive component and 5-15% of sodium bicarbonate component
Background
With the progress of urbanization in China and the enlargement of urban scale, the annual average growth rate of urban domestic garbage in China is as high as 8-10%, and the growth rate of some cities is even as high as 15-20%. According to the data of the national statistical bureau, the clear volume of domestic garbage in 2019 in China reaches 2.4 hundred million tons, the domestic garbage incineration is widely applied in China as the main process for treating and disposing the domestic garbage, 3.67 million tons of domestic garbage are incinerated in 2019 all over the country, and the quantity of garbage incineration plants is 389 seats.
The household garbage incineration technology realizes the harmlessness, reduction and recycling of garbage, the garbage volume can be reduced by about 80%, the garbage ton generated energy can reach 500 ℃, but the flue gas generated by garbage incineration contains a large amount of NOx, acid gas and a small amount of dioxin, and a flue gas treatment system is required for treatment.
The conventional NOx removal technology comprises SNCR (selective non-catalytic reduction) and SCR (selective catalytic reduction), the SNCR technology is adopted, the investment cost is low, the application is wide, the NOx removal efficiency is low and is generally 50% -80%, and the NOx emission value can be controlled to be 120-180 mg/Nm3 by adopting single SNCR in a conventional garbage incineration plant. By adopting the SCR technology, the investment cost is higher, the running cost of the SCR adopted in the household garbage incineration plant is also higher, but the NOx removal efficiency is high, the effect is more stable, and the NOx emission value can be controlled to be 50-80 mg/Nm 3. At present, the SNCR process is mainly adopted for waste incineration, but with the improvement of environmental protection requirements, the state department releases ' three-year action plan of winning blue sky guard war ' (national issue [2018]22 '), then the Hainan province releases ' domestic waste incineration pollution control standard ' (DB 46/484-2019), the Henan province releases ' implementation scheme of preventing and treating air, water and soil pollution in 2020 years in Henan province ' (Yun environmental attack [2020] 7), the Fujian province releases ' domestic waste incineration nitric oxide emission standard ' (DB 35/1976-2021), the SNCR process alone cannot meet the new emission standard requirements, and the SCR process is adopted to solve the problems of high investment cost and limited site aiming at the built domestic waste landfill, and the process propulsion is difficult to implement.
The ICR denitration process adopts solid addition, solid denitration agent is added at the temperature of 850-1000 ℃, and the solid denitration agent and the SNCR process are combined to form a new denitration process package, so that the aim of further controlling NOx is fulfilled, and the ICR denitration process is low in investment cost, small in occupied area and suitable for upgrading and transforming of an established incineration plant.
The key point of the ICR denitration process is research and development of a solid denitration agent and denitration efficiency, and the patent CN202010712879.8 provides the solid denitration agent and a preparation method thereof, wherein the solid denitration agent comprises 80-95 parts of a reducing agent, 1-5 parts of activated carbon and 0.01-0.2 part of hydrogen storage metal by mass, and the hydrogen storage metal is one of titanium, magnesium, zirconium and iron-titanium alloy. CN202010571059.1 proposes a high molecular solid powder denitration agent for flue gas denitration and a preparation method thereof, wherein the high molecular solid powder denitration agent comprises the following raw materials by weight percent: 10-70% of organic amino active compound, 10-40% of inorganic active amino compound, 5-40% of inorganic mineral powder, 5-30% of active mineral powder and 1-10% of additive. The obtained denitrifier is in a powder state. CN202010513240.7 proposes a solid denitration agent, which comprises the following raw materials in parts by weight: 1-15 parts of ferric oxide, 2-6 parts of manganese dioxide, 40-60 parts of urea, 10-25 parts of calcium magnesium acetate, 1-10 parts of titanium oxide and 5-10 parts of kaolin, wherein the particle size of the denitration agent powder is 50-70 nm. CN202010279226.5 proposes a composite denitrifier, which is mainly prepared from talcum powder, phyllosilicate, ferric oxide, lanthanum oxide, barium oxide, urea, oxidant, organic binder, inorganic binder, carboxymethyl cellulose, surfactant, dispersant, polyhydric alcohol and other raw materials. Iron oxide, lanthanum oxide, barium oxide and urea are used as denitration active components.
The method provides different formulas and methods for the denitration agent, but has the following defects:
1) the raw material part of the equipment is too expensive or difficult to obtain, so that the production of the denitration agent cannot be scaled, or the production cost of the denitration agent is too high, and the application of the product is influenced;
2) the production process of the denitration agent is complex, the steps are multiple, and no special large-scale production is available, so that the yield of the denitration agent is limited.
3) The denitration agent is powdery, so that the denitration agent is easy to block in the using process and the conveying link; the denitration agent is a mixture of powder and particles, and has the problems of uneven conveying and serious equipment blockage in the conveying link.
Disclosure of Invention
The invention aims to provide a granular ICR (intensive Care reactor) denitration agent component which can effectively solve the problems of blockage, production and application, effectively improve the removal efficiency of NOx and realize the stable standard-reaching emission of nitrogen oxides under the requirement of a new standard and a preparation method thereof.
In order to achieve the purpose, the invention adopts the following technical scheme:
a granular ICR denitration agent and a preparation method thereof are disclosed, and the granular ICR denitration agent is characterized by comprising a denitration agent, a catalyst, an adhesive and sodium bicarbonate, wherein the denitration agent comprises active ammonia, the catalyst, the adhesive and the sodium bicarbonate; the denitration agent comprises 40-90% of active ammonia component, 5-30% of catalyst component, 1-30% of adhesive component and 5-15% of sodium bicarbonate component.
Preferably, the active ammonia component is urea, ammonium bicarbonate or ammonia trimer.
Preferably, the catalyst component adopts titanium dioxide, vanadium pentoxide or zinc ferrite.
Preferably, the adhesive is polyurethane or polyacrylic resin.
The invention also provides a preparation method of the granular ICR denitration agent, which comprises the following steps: the method comprises the steps of selecting 40-90% of active ammonia components, 5-30% of catalysts, 1-30% of adhesives and 5-15% of sodium bicarbonate, and preparing the active ammonia components, the catalysts and the sodium bicarbonate into particles through a special denitration agent preparation system.
Preferably, the particle size of the denitration agent is 2-4 mm.
Preferably, the preparation temperature of the denitration agent is 850-1000 ℃.
Compared with the prior art, the invention has the technical effects that:
1) the denitration effect is excellent, the SNCR denitration efficiency is generally 50-60%, and after ICR denitration is adopted, the denitration efficiency can be improved to 80-90%;
2) the denitration agent has the advantages of low cost, simple production process, granular denitration agent, material conveying convenience and no blockage in the material conveying process.
Detailed Description
The technical solutions in the embodiments of the present invention will be described clearly and completely with reference to the following embodiments of the present invention, and it is obvious that the described embodiments are only a part of the embodiments of the present invention, and not all of the embodiments.
The invention discloses a granular ICR denitration agent and a preparation method thereof. A particulate ICR denitrifier comprises active ammonia, a catalyst, a binder and sodium bicarbonate; the denitration agent comprises 40-90% of active ammonia component, 5-30% of catalyst component, 1-30% of adhesive component and 5-15% of sodium bicarbonate component.
Further, the active ammonia component adopts urea, ammonium bicarbonate or ammonia trimer.
Further, the catalyst component adopts titanium dioxide, vanadium pentoxide or zinc ferrite.
Further, the adhesive is polyurethane or polyacrylic resin.
The invention also provides a preparation method of the granular ICR denitration agent, which comprises the following steps: the method comprises the steps of selecting 40-90% of active ammonia components, 5-30% of catalysts, 1-30% of adhesives and 5-15% of sodium bicarbonate, and preparing the active ammonia components, the catalysts and the sodium bicarbonate into particles through a special denitration agent preparation system.
Further, the particle size of the denitration agent is 2-4 mm.
Further, the preparation temperature of the denitration agent is 850-1000 ℃.
The sodium bicarbonate component adopted by the invention is beneficial to removing acid gas in the flue gas and synchronously realizing the deacidification effect.
Examples
The preparation of the denitration agent adopts 84% of active ammonia, 5% of catalyst, 1% of adhesive and 10% of sodium bicarbonate.
Wherein the active ammonia is urea; the catalyst adopts titanium dioxide and zinc ferrite, and the proportion is 4: 1; the adhesive is polyurethane; the sodium bicarbonate is industrial sodium bicarbonate.
The components of the denitration agent are mixed and then prepared into particles by a special denitration agent preparation system, and the particle size of the denitration agent is 2-4 mm.
The denitration agent prepared by the invention is applied to a certain household garbage incineration plant, and the basic parameters of the incineration plant are as follows in the following table 1:
TABLE 1
Serial number
|
Name (R)
|
Parameter(s)
|
Remarks for note
|
1
|
Grate type
|
Horizontal incinerator
|
|
2
|
Throughput of treatment
|
500d/t
|
|
3
|
Number of boilers
|
3
|
|
4
|
Amount of flue gas (design value)
|
90260Nm3/h
|
Single table
|
5
|
Boiler inlet temperature
|
>850℃
|
|
6
|
Oxygen content of flue gas
|
5-8%
|
|
7
|
Initial concentration of NOx
|
400mg/Nm3
|
Dry basis, 11% O2
|
8
|
NOx emission after SNCR denitration means
|
<180mg/Nm3
|
Dry basis, 11% O2 |
After the ICR denitration process is adopted, the operation is continued for 3 months, the dosage of the denitration agent is controlled within 0.8-1.2 kg/t of garbage, and from the operation data of Table 2, the ammonia escape is controlled within 8mg/Nm3, the NOx is controlled within 100mg/Nm3, and the removal rate of the NOx reaches 80-90%.
TABLE 2
It can be seen that the present invention compares with the prior art:
1) the denitration effect is excellent, the SNCR denitration efficiency is generally 50-60%, and after ICR denitration is adopted, the denitration efficiency can be improved to 80-90%;
2) the denitration agent has the advantages of low cost, simple production process, granular denitration agent, material conveying convenience and no blockage in the material conveying process.
The above description is only for the preferred embodiment of the present invention, but the scope of the present invention is not limited thereto, and any person skilled in the art should be considered to be within the technical scope of the present invention, and the technical solutions and the inventive concepts thereof according to the present invention should be equivalent or changed within the scope of the present invention.