CN202087235U - Multi-level thermolysis coupling denitrification device with pre-flow field equalizing device - Google Patents

Abstract

The utility model discloses a multi-stage pyrolysis coupling denitrification device with a front flow field uniform device, which optimizes the uniformity of NOx in the furnace section by installing the front flow field uniform device; in boilers with different flue gas temperatures Different forms and different numbers of reductant ammonia supplementing spray guns are arranged in different positions of the flue gas passage to control the corresponding uniform distribution of NOx and NH ₃ ; an SCR reactor loaded with an SCR catalyst is installed in the tail flue of the boiler. The comprehensive denitrification efficiency of the utility model reaches more than 90%, which saves the amount of SCR catalyst, and reduces the usage of reducing agent by improving the utilization efficiency of reducing agent in the selective non-catalytic reduction reaction zone, effectively controlling the escape of ammonia; It is suitable for all kinds of boilers and industrial furnaces and has broad application prospects through the transformation of the existing boiler denitrification project.

Description

A multi-stage pyrolysis coupled denitrification device with a pre-flow field uniform device

technical field

The utility model relates to a pollutant discharge control device for coal-fired boilers, in particular to a multi-stage thermolysis coupling denitrification device with a front flow field uniform device.

Background technique

Nitrogen oxides NOx include N ₂ O, NO, NO ₂ , N ₂ O ₃ , N ₂ O ₄ and N ₂ O ₅ , and are considered to be one of the main sources of air pollution. Among them, NO and NO ₂ are important air pollutants, and almost all nitrogen oxides produced in combustion are NO and NO ₂ . 70% of my country's total nitrogen oxide emissions come from direct combustion of coal, and the power industry is a large coal-burning household in my country, so the main source of NOx emissions is thermal power plants. The increasingly stringent environmental regulations require that NOx emission reduction methods be applied to NOx emission sources, especially power plant boilers, in order to control the total emission of nitrogen oxides. The existing methods for reducing nitrogen oxides emissions in coal-fired power plants are mainly two methods: control during combustion and flue gas denitrification after combustion. The NOx control method in the combustion process is mainly to reduce NOx emissions by changing the burner structure and combustion conditions. It is the most widely used, economical and effective method, and can be used in conjunction with other denitrification methods. The flue gas denitrification methods applied to coal-fired boilers mainly include selective non-catalytic reduction (SNCR) and selective catalytic reduction (SCR). The SNCR method has a simple system, simple construction, low initial investment, and low operating cost, but its biggest defect is the low denitrification rate, which is only 30-50% in power plant coal-fired boilers, and the SNCR method is difficult for ammonia to escape. Control, affecting the stability and safety of boiler operation. The SCR method has high denitrification efficiency. Because the mixer, ammonia injection grid and flue gas rectifier can well realize the uniform mixing of reducing agent and NO in flue gas, the denitrification rate can reach more than 95%, but its disadvantage is that it occupies an area Large, complex system, large initial investment, high operating cost. Mixed SNCR-SCR denitrification technology is also used in coal-fired boilers, but it is difficult to achieve uniform mixing of reducing agent and NO in flue gas, so the denitrification rate of SNCR-SCR method is not satisfactory.

Utility model content

The purpose of the utility model is to provide a multi-stage pyrolysis coupling denitrification device with a pre-flow field uniform device.

In order to achieve the above purpose, the technical solution adopted by the utility model is: the multi-stage pyrolysis coupling denitrification device with a pre-flow field uniform device is equipped with a pre-flow field uniform device on the boiler furnace, and a pre-flow field uniform device is installed on the front wall of the boiler There are more than one layer of reducing agent ammonia supplementing spray guns fixedly arranged, and more than one layer of reducing agent ammonia supplementing spray guns are arranged in the horizontal flue of the boiler, and the SCR reactor carrying the SCR catalyst is fixedly installed at the tail flue of the boiler.

Further, the boiler front wall of the utility model is used to arrange the temperature of the flue gas at the position where the reducing agent supplementing ammonia spray gun is 750-950°C, and the horizontal flue of the boiler is used to arrange the flue gas at the position where the reducing agent supplementing ammonia spray gun is arranged. The temperature is 650-800°C.

Furthermore, the front flow field uniform device described in the utility model is a swingable tuyere arranged on the furnace of the boiler.

Compared with the prior art, the utility model has the following advantages:

(1) The utility model adopts a front flow field uniform device. In particular, if the front flow field uniform device is a swingable tuyere installed on the boiler furnace, the NOx and The distribution of flue gas velocity and temperature in the furnace meets the requirements of the SCR system for the uniformity of flue gas and reducing agent mixing under the premise of a limited number of ammonia replenishing spray guns;

(2) The utility model rationally arranges more than one layer of reducing agent ammonia replenishing spray guns on the front wall of the boiler with a flue gas temperature range of 750-950°C, and the horizontal flue gas of the boiler with a flue gas temperature range of 650-800°C More than one layer of reductant ammonia replenishing spray guns are arranged in the duct, and the reducing agent ammonia replenishing spray guns installed at different positions with different flue gas temperatures adopt different structural forms, and the flow rate of the reducing agent sprayed by each spray gun can be adjusted independently. Arranging the SCR reactor in the end improves the utilization rate of the selective non-catalytic reduction reaction of the reducing agent sprayed into the furnace, and makes the NH ₃ and NO generated after the pyrolysis of the reducing agent better uniformly distributed, which is The selective catalytic reduction reaction that occurs on the surface of the SCR catalyst in the downstream SCR reactor provides extremely favorable factors;

(3) The utility model adopts the pyrolysis system of the ammonia replenishing spray gun, rationally utilizes the boiler flue, does not need space limitation, simple equipment, and saves the complex reductant injection system of the SCR system;

(4) The reductant ammonia replenishing spray gun sprays the reductant into the furnace, and part of the reductant undergoes selective non-catalytic reduction reaction, which initially reduces the NO in the flue gas entering the SCR reactor, so the SCR reactor only needs to arrange a layer of catalyst , which greatly reduces the operating cost of the SCR system, saves the space occupied by the SCR system, and is easy to transform into the utility model on the basis of the existing boiler denitrification project;

(5) The comprehensive denitrification rate of the method of the utility model is more than 90%, and the operating cost is lower than the existing pure SCR denitrification method. It is suitable for burning various boilers and kilns, and has broad application prospects.

Description of drawings

Fig. 1 is the schematic diagram of the principle of the utility model;

Fig. 2 is the structural schematic diagram of setting the reductant ammonia replenishment spray gun on the front wall of the boiler;

Fig. 3 is a schematic diagram of the swing tuyere of the front flow field uniform device of the present invention, wherein α is an adjustable swing angle.

Detailed ways

The following is a further detailed description of the multi-stage pyrolysis coupling denitrification method with a pre-flow field uniform device of the present invention according to the accompanying drawings and specific examples.

As shown in Figures 1 to 3, in the multi-stage pyrolysis coupling denitrification device of the utility model, a pre-flow field uniform device is installed on the boiler furnace, and more than one layer of reducing agent and ammonia replenishing spray guns 3 are fixedly arranged on the front wall of the boiler In the horizontal flue of the boiler, more than one layer of reducing agent ammonia replenishing spray guns is arranged, and the SCR reactor carrying the SCR catalyst is fixedly installed at the tail flue of the boiler. As a preferred solution of the utility model, the front flow field uniform device is a swingable tuyere arranged on the furnace of the boiler. In particular, it is preferable that the reducing agent ammonia replenishing spray gun 3 is arranged at the position where the flue gas temperature of the boiler front wall is 750-950°C, and the reducing agent ammonia replenishing spray gun 4 is arranged at the position where the flue gas temperature of the horizontal flue of the boiler is 650-800°C. location.

As shown in Figure 3, as a simple and feasible preferred embodiment of the present invention, when the front flow field uniform device 2 is a swing tuyere 21 located in the furnace of the boiler, the angle of the swing tuyere 21 can be adjusted , select different layers of reductant ammonia replenishment spray guns to be put into operation, and individually control the flow rate of each spray gun to inject reductant, effectively realize the uniform mixing of reductant and NO in flue gas, to meet the requirements of NOx under different loads of coal-fired boilers Control requirements, stable and reliable, high efficiency. The utility model promotes and improves the mixing uniformity of NH3 and NO in the flue gas by individually adjusting the injection amount of the reducing agent of each spray gun and adopting different types of spray guns, adjusting the angle of the wind, and promoting and improving the uniformity of mixing of _NH3 and NO in the flue gas, which is helpful for eliminating the outlet of the furnace. The non-uniform distribution of NO concentration caused by rotation deviation has a significant effect on the non-uniform mixing of _NH3 and it.

Specifically, as shown in Fig. 1 and Fig. 2, a pre-flow field uniform device 2 is provided on the furnace 1 of the boiler. If the front flow field uniform device is provided with four swinging tuyere 21 that can swing left and right as shown in Figure 3, the direction of the airflow coming out of the tuyere can be changed to adjust the NOx and flue gas velocity and temperature in the furnace. distribution in . The upper part of the furnace 1 is fixedly installed with the reducing agent ammonia replenishing spray gun 3 and the reducing agent ammonia replenishing spray gun 4: Among them, the reducing agent ammonia replenishing spray gun 3 is fixedly arranged on the front wall of the boiler in a single layer, and a multi-hole type spray gun is generally used; The ammonia spray gun 4 is fixedly arranged between the high-temperature superheater and the high-temperature reheater in the upper horizontal flue of the furnace. There are 4 spray guns arranged symmetrically on the left and right side walls in two layers. V-shaped nozzle spray guns are generally used. Among them, the reducing agent ammonia replenishing spray gun 3 is arranged at the position where the flue gas temperature of the boiler front wall is 750-950°C, and the reducing agent ammonia replenishing spray gun 4 is arranged at the position where the flue gas temperature of the horizontal flue of the boiler is 650-800°C . In the present utility model, the reducing agent ammonia replenishing spray gun 3 and the reducing agent ammonia replenishing spray gun 4 can be arranged in one or more layers. In addition, an SCR reactor 9 loaded with an SCR catalyst is fixedly installed at the tail flue of the boiler, and the reducing agent is an ammonia-containing liquid.

When using the device of the utility model for denitrification, according to the load of the boiler and the flue gas temperature at the reducing agent ammonia replenishing spray gun, it is determined whether to use the reducing agent ammonia replenishing spray gun 3 on the front wall of the boiler or the reducing agent ammonia replenishing spray gun in the horizontal flue The spray gun 4 atomizes the reducing agent and sprays it into the furnace 1, so that a part of the reducing agent sprayed into the furnace 1 undergoes a selective non-catalytic reduction reaction with NO in the flue gas, and the reducing agent sprayed into the furnace 1 The rest of it is pyrolyzed into ammonia gas; then the ammonia gas mixes with the flue gas in the furnace and flows to the tail flue and gradually mixes evenly. When the flue gas mixed with ammonia gas flows through the SCR reactor 9 , NO in the flue gas is reduced to N ₂ after selective catalytic reduction reaction with ammonia gas on the surface of the SCR catalyst.

Further examples are given below:

For a 420t/h coal-fired boiler under a load of 60-110MW, NOx of about 450mg/ ^Nm3 is generated through low-nitrogen combustion in the furnace, and flows upward with the flue gas. The distribution of NOx on the cross-section 14 in the furnace is optimized by adjusting the angle of the swing-type tuyere 21 provided in the furnace of the boiler. As shown in Figure 2, by fine-tuning the manual ball valve 19 of each ammonia replenishing spray gun, observing the reading of the float flow meter 20, adjusting the flow rate of the reducing agent 18 through the ammonia replenishing spray gun, and maintaining the atomized compressed air 16 at the local pressure gauge 15 The displayed value is above 0.55MPa, and at the same time, the value of the local pressure gauge 17 of the reducing agent is maintained above 0.55MPa, so that the concentration of NOx and the concentration of decomposed NH ₃ are uniformly distributed. It should be noted that, in addition to using compressed air to atomize the reducing agent, superheated steam may also be used to atomize the reducing agent. The temperature range of the flue gas at the elevation 3 of the reductant ammonia replenishing spray gun is 780-900°C, and the temperature range of the flue gas at the elevation 4 of the reducing agent ammonia replenishing spray gun is 620-690°C. Based on the fact that the load of the coal-fired boiler in this embodiment is 60-110 MW, the reducing agent ammonia replenishing spray gun 3 can be put into operation at this time, and the reducing agent ammonia replenishing spray gun 4 cannot be put into operation. The reducing agent is preferably a urea solution with a concentration of 10%. The molar ratio of the injection amount of the reducing agent (calculated according to the total pyrolysis to NH ₃ ) to the NO in the flue gas is 1.0-1.8:1, which is supplemented by the reducing agent on the front wall. The ammonia spray gun 3 is sprayed into the furnace, and part of the reducing agent in it undergoes selective non-catalytic reduction reaction with NO in the flue gas. After the non-catalytic reduction reaction, the concentration of NOx can be reduced by about 37%, reaching about 280 mg/ ^Nm3 ; The rest of the reducing agent is pyrolyzed into NH ₃ , and the NH ₃ in the flue gas is about 118ppm. The flue gas containing NH ₃ passes through different heat exchange surfaces, the tail flue, the diverting flue, the deflector 5, and the rectifier above the SCR catalyst 6. Make the NH ₃ and the NO in the flue gas fully mixed evenly, so that a selective catalytic reduction reaction occurs on the surface of the SCR catalyst 7 to reduce the NO in the flue gas to N ₂ . The time from the beginning of mixing the ammonia gas and the flue gas in the furnace to reaching the SCR reactor 9 is usually more than 3 seconds. The temperature range of the flue gas where the SCR reactor 9 is located is 289-307° C., and the bottom of the SCR reactor 9 is a catalyst reserved layer 8 . After passing through the SCR reactor 9, the NOx concentration in the flue gas is reduced to about 50 mg/Nm ³ , and the average ammonia escape concentration of the system is controlled below 3ppm. The denitrified flue gas passes through an air preheater 10, a dust collector 11, a desulfurization device 12, and then is discharged into the atmosphere through a chimney 13.

For a 420t/h coal-fired boiler under a load of 120-125MW, NOx of about 440mg/ ^Nm3 is generated through low-nitrogen combustion in the furnace, and flows upward with the flue gas. By adjusting the angle of the oscillating air 21 installed in the furnace of the boiler, the distribution of NOx in the furnace is matched with the individual flow adjustment of the reducing agent ammonia replenishing spray gun, so that the concentration of NOx and the concentration of decomposed _NH3 are uniformly distributed. The temperature range of the flue gas at the elevation of the 3rd position of the reductant ammonia replenishing spray gun is 840-970°C, and the flue gas temperature range of 704-740°C at the elevation of the 4th position of the reducing agent ammonia replenishing spray gun. At this time, the reducing agent ammonia replenishing spray gun 4 can be put into operation alone or the reducing agent ammonia replenishing spray guns 3 and 4 can be put into operation simultaneously. The reducing agent is urea solution with a concentration of 10%. The molar ratio of the injection amount of the reducing agent (calculated according to the total pyrolysis to NH ₃ ) to the NO in the flue gas is 1.0-1.8:1, which is supplemented by the reducing agent in the horizontal flue. The ammonia spray gun 4 or the reductant ammonia supplement spray gun 3 on the front wall of the boiler and the reductant 4 in the horizontal flue are jointly sprayed into the furnace, wherein, a part of the reductant and the NO in the flue gas undergo selective non-catalytic reduction, and through this non-reductive After the catalytic reduction reaction, the concentration of NOx can be reduced by about 39%, reaching about 270 mg/ ^Nm3 ; the rest of the reducing agent is pyrolyzed into _NH3 , and the _NH3 in the flue gas is about 120ppm. The flue gas containing _NH3 passes through different The heat exchange surface, the tail flue, the turning flue, the deflector 4, and the rectifier 5 above the SCR catalyst make the NH ₃ and the NO in the flue gas fully mixed evenly, so that a selective catalytic reduction reaction occurs on the surface of the SCR catalyst 6 to make the flue gas NO in the gas is reduced to N ₂ . The time from the beginning of mixing the ammonia gas and the flue gas in the furnace to reaching the SCR reactor 9 is usually more than 3 seconds. The temperature range of the flue gas where the SCR reactor 9 is located is 304-314°C. After passing through the SCR reactor 9, the NOx concentration in the flue gas is reduced to about 35mg/Nm ³ , and the average ammonia slip concentration of the system is controlled below 3ppm.

After the method of the utility model is applied in practice, it can not only effectively reduce the emission of nitrogen oxides from coal-fired boilers, the efficiency can reach more than 90%, and it is easy to operate and control, and can remove high-efficiency NOx at low cost to meet the increasingly stringent requirements of environmental regulations.

Claims (3)

1. multistage pyrolysis coupling denitrification apparatus with preposition even flow field device, it is characterized in that: on boiler furnace, be provided with preposition even flow field device, stationary cloth is equipped with the above reducing agent of one deck and mends the ammonia spray gun on the boiler front wall, in boiler horizontal gas pass, be furnished with the above reducing agent of one deck and mend the ammonia spray gun, be loaded with the SCR reactor of SCR catalyst in the fixed installation of boiler back end ductwork place.

2. multistage pyrolysis coupling denitrification apparatus according to claim 1, it is characterized in that: in the flue-gas temperature of described boiler front wall is that 750～950 ℃ position arranges that described reducing agent mends the ammonia spray gun, is that 650～800 ℃ position arranges that described reducing agent mends the ammonia spray gun in the flue-gas temperature of described boiler horizontal gas pass.

3. multistage pyrolysis coupling denitrification apparatus according to claim 1 and 2 is characterized in that: but described preposition even flow field device is the swing type air port of being located on the boiler furnace.

Images