CN209386820U

CN209386820U - A kind of production system of pelletizing flue gas ultra-low NOx emission

Info

Publication number: CN209386820U
Application number: CN201821580968.6U
Authority: CN
Inventors: 魏进超; 叶恒棣; 崔泽星
Original assignee: Zhongye Changtian International Engineering Co Ltd
Current assignee: Zhongye Changtian International Engineering Co Ltd
Priority date: 2018-09-27
Filing date: 2018-09-27
Publication date: 2019-09-13
Anticipated expiration: 2028-09-27

Abstract

The utility model proposes a kind of production systems of pelletizing flue gas ultra-low NOx emission, add a set of smoke circulating system, are further transported to using the flue gas being discharged from down-draft drying zone as cooling wind: cold two sections of the air inlet of ring；Simultaneously: being equipped with reduction activator jetting device, reducing agent and the NO in the flue gas after cold two sections of ring being located at cold two sections of the top of ring_xSNCR denitration is realized in reaction；Alternatively, being delivered to the preheated one-section of drying grate again after SNCR processing system from the gas that the cold two sections of air outlets of ring are discharged.Using the high temperature feature from down-draft drying zone discharge flue gas, while using the condition of high temperature sinter in cold two sections of ring, which is handled using SNCR.Using above-mentioned technological means, a degree of can reduce enterprise's Air Pollutant Emission limit value to the production pressure of pellet roasting equipment requirement, have " it is with low investment, operating cost is low, NO_xEmission reduction effect is significant " the characteristics of.

Description

A kind of production system of pelletizing flue gas ultra-low NOx emission

Technical field

The utility model relates to a kind of pelletizing production technologies, and in particular to a kind of production of pelletizing flue gas ultra-low NOx emission System belongs to pelletizing production, environmental protection technical field.

Background technique

Pellet is the main iron-containing charge of China's blast furnace ironmaking, and China's pellet yield in 2015 is 128,000,000 tons.Phase Than sinter, since low energy consumption, environment is relatively friendly for pelletizing production process, and product is with intensity is good, grade is high, metallurgical performance Good advantage, increasing And Coke-saving can be played, improve ironmaking technology economic indicator, reduce pig iron cost, mention by being applied in blast furnace process The effect of high economic benefit, therefore pellet is greatly developed recent years in China.

For China's pelletizing production based on grate kiln technique, yield accounts for 60% or more of pelletizing total output.In recent years Come, with increasingly sophisticated, the raising (maturing temperature is caused to increase) of bloodstone ratio, low-rank fuel of iron ore raw material and fuel Scale utilize, the application of the nitrogenous coke-stove gas of gas base rotary kiln etc. so that many enterprise pelletizing production process NO_xConcentration of emission It is in rising trend；In addition increasingly harsh, the NO that Environmental Protection in China requires_xDischarge is included into the checking system of discharge.NO_xIt is to form light The main reason for chemical fumes, acid rain, haze weather, aggravation depletion of the ozone layer and promotion greenhouse effects, ecological environment is endangered It is huge.From 2015, pelletizing production NO_x(with NO₂Meter) emission limit 300mg/m³, so that Some Enterprises need to add denitration Facility is just able to satisfy the discharge standard of country.In June, 2017, State Ministry of Environmental Protection issued " steel sintering, pelletizing industrial atmosphere dirt Contaminate object discharge standard " revision bulletin, by NO_x(with NO₂Meter) emission limit is from 300mg/Nm³It is adjusted downward to 100mg/Nm³, sintering It is 16% with pellet roasting flue gas benchmark oxygen content.

Although a large amount of work has been done in environmental protection by pelletizing enterprise, dedusting and desulfurization have obtained effective control, Neng Gouman Sufficient emission request, but current NO_xAt high cost, complex process is removed, under the environment of steel form depression, this gives pelletizing industry New challenge is brought, Some Enterprises are because of NO_xExceeded a large amount of underproduction of having to, or even face and shut down.From current most of ball From the point of view of group's condition of production, NO_xGeneral concentration of emission is in 200~400mg/m³If NO can be reduced from source and process_xIt produces It is raw, so as to meet emission request, then end denitration cleaning equipment can be saved, grate-kiln pelletizing is produced and is anticipated Justice is great, is conducive to the vitality and competitiveness that further increase pelletizing enterprise.

The method of existing removing nitrogen oxides in effluent mainly selective catalytic reduction technique (SCR) and non-selective is urged Change reduction technique (SNCR).Wherein, temperature plays a leading role to SNCR denitration technology.It is generally acknowledged that temperature range be 800 DEG C~ 1100 DEG C are more suitable for, when the temperature is excessively high, NH₃Oxidation generates NO, and the concentration that may cause NO increases, and leads to NO_xRemoval efficiency It reduces；When the temperature is too low, NH₃Reaction rate decline, NO_xRemoval efficiency can also decline, while NH₃Escape amount also will increase. Usually the temperature range of preheating two sections (PH) is 850 DEG C~1000 DEG C, meets the condition of SNCR denitration method, but needs to optimize control System can be only achieved optimal emission reduction effect.

The selectivity of SCR denitration technology refers in the effect of catalyst and under oxygen existence condition, NH₃Preferential and NO_xHair It survives former elimination reaction, generates N₂And H₂O, and the oxygen in flue gas of getting along well carries out oxidation reaction.

NO_xGeneration be mostly derived from two kinds of forms of fuel type and heating power type, reduce coal gas or pulverized coal injection although can pass through Enter amount, reduces kiln temperature, and use lower NO_xRaw material and the measures such as fuel reduce grate-kiln pelletizing Production process NO_xProduction quantity, but to the buying of crude fuel, the optimization of process system and the selection of change system require seem Excessively harsh, once production process is unstable, it will cause NO_xIt is exceeded, how from process flow and NO_xDecomposition mechanism Hand reduces grate-kiln pelletizing production process NO_xDischarge be this patent technical problems to be solved.

In order to meet grate-kiln pelletizing production process NO_xEmission request, the energy-saving and emission-reduction for responding country are called, It is the characteristics of more advanced air circulation must being gone out from process flow, utility model, while utilizing system itself, real Existing low NO_xPelletizing production.

Utility model content

Aiming at the problems existing in the prior art, in order to solve pelletizing production process NO_xDischarge is not up to standard and in end It adds the enterprises such as denitrification apparatus somewhat expensive and is difficult to the problem of receiving, a set of smoke circulating system is added in this patent proposition, will be from The flue gas of down-draft drying zone discharge is further transported to as cooling wind: cold two sections of the air inlet of ring；Simultaneously: being located at, ring is cold Two sections of top sprays into reducing agent, reducing agent and the NO in the flue gas after cold two sections of ring_xSNCR denitration is realized in reaction；Or The gas of person, the discharge of bis- sections of air outlets of Cong Huanleng are delivered to the preheated one-section of drying grate again after SNCR processing system.It utilizes From the high temperature feature of down-draft drying zone discharge flue gas, while using the condition of high temperature sinter in cold two sections of ring, at SNCR Manage the partial fume.Using above-mentioned technological means, can a degree of reduction enterprise Air Pollutant Emission limit value to pelletizing Roasting apparatus require production pressure, have " it is with low investment, operating cost is low, NO_xEmission reduction effect is significant " the characteristics of.

According to the first embodiment provided by the utility model, a kind of production of pelletizing flue gas ultra-low NOx emission is provided Technique.

A kind of production technology of pelletizing flue gas ultra-low NOx emission, the production technology the following steps are included:

1) green-ball is on drying grate successively by two sections of blasting drying period, down-draft drying zone, preheated one-section and preheating progress Dry, preheating, roasts subsequently into passing through in rotary kiln, then successively by ring is one section cold, ring is two sections cold, ring is cold on ring cold machine Three sections and cold four sections of ring are cooled down, and acid pellet is obtained；

2) it is increased by cold one section of ring of cooling wind temperature, the wind of the cold one section of discharge of ring is delivered in rotary kiln and participates in ball Group's roasting, the hot wind discharged from rotary kiln are delivered to two sections of preheating of drying grate；The hot wind carries out in two sections of preheating with green-ball Down-draft drying zone is delivered to after heat exchange；

3) it is increased by cold two sections of ring of cooling wind temperature, the wind of the cold two sections of discharges of ring is delivered to the preheating one of drying grate Section, and heat exchange is carried out with green-ball in preheated one-section, preheat green-ball；

4) it is increased by cold three sections of ring of cooling wind temperature, the air blast that the wind of the cold three sections of discharges of ring is delivered to drying grate is done Dry section, and heat exchange is carried out with green-ball in blasting drying period, then it is discharged from the exhaust outlet of blasting drying period；

Wherein: the flue gas being discharged from down-draft drying zone is further transported to as cooling wind: cold two sections of the air inlet of ring； Simultaneously:

Reducing agent, reducing agent and the NO in the flue gas after cold two sections of ring are sprayed into being located at cold two sections of the top of ring_xInstead It answers, realizes SNCR denitration；It combs alternatively, being delivered to chain again after SNCR processing system from the gas that the cold two sections of air outlets of ring are discharged The preheated one-section of machine.

Preferably, the technique further include: step 5) separates a part as cooling from the flue gas that down-draft drying zone is discharged Wind is further transported to: cold three sections of the air inlet of ring；Simultaneously:

Reducing agent, reducing agent and the flue gas being discharged from down-draft drying zone are sprayed into the position for being located at the cold three sections of bottom bellows of ring In NO_xSCR denitration is realized in reaction；Alternatively, the gas being discharged from the cold three sections of air outlets of ring is defeated again after SCR processing system It send to the blasting drying period of drying grate.

Preferably, the technique further include: the gas that step 6) is discharged from preheated one-section is further defeated as cooling wind It send to ring cold one section of air inlet.

Preferably, in two sections of preheating, position above green-ball sprays into reducing agent, reducing agent and enters preheating two NO contained in hot wind in section_xSNCR denitration is realized in reaction.

Preferably, hot wind preheating two sections in and green-ball carry out heat exchange after, the gas of discharge after SCR is handled again It is delivered to down-draft drying zone.

Preferably, hot wind is in two sections of preheating and after green-ball carries out heat exchange, the gas of discharge by dust removal process it Afterwards, then SCR processing is carried out.

Preferably, hot wind is in two sections of preheating and after green-ball carries out heat exchange, the gas of discharge by dust removal process it Afterwards, by residual heat using device, SCR processing is then carried out again.

Preferably, the gas being discharged from the cold two sections of air outlets of ring is by residual heat using device, then using SNCR at Reason system realizes SNCR denitration.

Preferably, then the gas being discharged from the cold three sections of air outlets of ring is handled by residual heat using device using SCR System realizes SCR denitration.

Preferably, the gas after the cold four sections of heat exchange of ring is used for pneumatic conveying, Tuo Bai or discharge.

Preferably, the gas after blasting drying period exchanges heat is used for pneumatic conveying, Tuo Bai or discharge.

Preferably, the portion gas of down-draft drying zone and preheated one-section is used for pneumatic conveying, Tuo Bai or discharge.

Preferably, being delivered to ring again after desulfurization process and/or dust collecting process from the flue gas that down-draft drying zone is discharged Cold two sections and/or cold three sections of ring.

Preferably, it is cold to be delivered to ring again after desulfurization process and/or dust collecting process from the flue gas that preheated one-section is discharged One section.

According to second of embodiment provided by the utility model, a kind of production of pelletizing flue gas ultra-low NOx emission is provided System.

The production system of a kind of pelletizing flue gas ultra-low NOx emission or for being produced described in any one of the first embodiment The pelletizing production system of technique, the system include: drying grate, rotary kiln, ring cold machine.Wherein: being moved towards according to technique, the chain is combed Machine is disposed with two sections of blasting drying period, down-draft drying zone, preheated one-section and preheating.Ring cold machine is disposed with ring cold one Section, ring it is two sections cold, cold three sections and cold four sections of ring of ring.Two sections of the preheating and other end connection ring of the tail end connection drying grate of rotary kiln Cold one section of the ring of cold.

Wherein: cold one section of the air outlet of ring is connected to the air inlet of rotary kiln, the air outlet of rotary kiln via first pipe The air inlet of two sections of preheating is connected to via second pipe, the air outlet of two sections of preheating is connected to exhausting drying by third pipeline The air inlet of section.

Cold two sections of the air outlet of ring is connected to the air inlet of preheated one-section via the 4th pipeline；Cold three sections of the air outlet warp of ring The air inlet of blasting drying period is connected to by the 5th pipeline.

Wherein: the air outlet of down-draft drying zone is connected to cold two sections of the air inlet of ring via the 6th pipeline；Simultaneously:

It is equipped with the first reducing agent jetting device positioned at cold two sections of the top of ring, alternatively, the 4th pipeline is equipped with SNCR processing System.

Preferably, it is the 7th pipeline that the 6th pipeline, which separates one article of branch,.7th pipeline is connected to cold three sections of the air inlet of ring Mouthful；Simultaneously:

It is equipped with the second reducing agent jetting device positioned at the position of the cold three sections of bottom bellows of ring, alternatively, the 5th pipeline is equipped with First SCR processing system.

Preferably, the air outlet of preheated one-section is connected to cold one section of the air inlet of ring via the 8th pipeline.

Preferably, being equipped with third reducing agent jetting device positioned at the top of green-ball charge level in two sections of preheating.

Preferably, third pipeline is equipped with the 2nd SCR processing system.

Preferably, being additionally provided with the first dust-extraction unit on third pipeline, and the first dust-extraction unit is located at the 2nd SCR processing The upstream of system.

Preferably, the 6th pipeline be equipped with the second dust-extraction unit and the first desulfurizer, and the second dust-extraction unit and The upstream for separating the 7th pipeline location is arranged in first desulfurizer.

Preferably, the 8th pipeline is equipped with third dust-extraction unit and the second desulfurizer.

Preferably, third pipeline is equipped with the first residual heat using device, and the setting of the first residual heat using device is the Between one dust-extraction unit and the 2nd SCR processing system.

Preferably, the 4th pipeline is equipped with the second residual heat using device, and the setting of the second residual heat using device exists The upstream of SNCR processing system.

Preferably, the 5th pipeline is equipped with third residual heat using device, and the setting of third residual heat using device is the The upstream of one SCR processing system.

In the present invention, the first residual heat using device, the second residual heat using device, third residual heat using device be respectively Solely it independently is heat exchanger or wastewater treatment equipment.

Preferably, heat exchanger is pipe heat exchanger.Wastewater treatment equipment includes that gas access, gas vent, waste water enter Mouth, atomizer.

In the present invention, ring is one section cold, ring is two sections cold, the air inlet of ring cold three sections and the cold four sections of bottoms of ring and wind Machine connection.

In the present invention, cold four sections of the air outlet of ring is connect with the 9th pipeline.9th pipeline is connected to chimney.

In the present invention, the air outlet of blasting drying period is connect with the tenth pipeline.Tenth pipeline is connected to chimney.

Preferably, the Article 2 branch that the 6th pipeline separates is the 11st pipeline.One article of branch that 8th pipeline separates For the 12nd pipeline.11st pipeline and the 12nd pipeline are connected to chimney.

Preferably, merging some or all of in the 11st pipeline, the 12nd pipeline, the 9th pipeline, the tenth pipeline After be connected to chimney.

In pelletizing process, NO_x(nitrogen oxides) mainly generates in rotary kiln, and the gas in rotary kiln is by two sections of preheating After be delivered to down-draft drying zone, the gas direct emission that down-draft drying zone air outlet is discharged in the prior art, therefore, chimney row The NO in gas put_xIt is mainly derived from the gas of down-draft drying zone discharge.In this technique, the position Jun Ji of live gas is inputted In in ring cold machine.Cold one section of the gas of ring is inputted, enters rotary kiln after the sinter heat exchange in cold one section of ring, carries out a little Fire burning, consumption input the oxygen in gas.Cold two sections of the gas of ring is inputted, after the sinter heat exchange in cold two sections of ring It is delivered to preheated one-section, in the prior art, gas of the gas of preheated one-section air outlet discharge directly with down-draft drying zone discharge Pass through smoke stack emission after merging；The content of nitrogen oxides is higher from the gas that down-draft drying zone is discharged, and arranges from preheated one-section Oxygen content is higher in gas out, and mixing is more than the gas of 16% high amount of nitrogen oxides for oxygen content later.It is cold to input ring Three sections and cold four sections of the gas of ring, after the sinter in cold three sections and cold four sections of ring of ring exchanges heat respectively, due to the part Sinter temperature it is relatively low, the content of nitrogen oxides is few, and the gas of elevated oxygen level is also fully able to reach nitrogen after heat exchange The discharge standard of oxide.

In June, 2017, State Ministry of Environmental Protection issued the revision of " steel sintering, pelletizing industrial air pollution object discharge standard " Bulletin, by NO_x(with NO₂Meter) emission limit is from 300mg/Nm³It is adjusted downward to 100mg/Nm³, sintering and pellet roasting flue gas benchmark contain Oxygen amount is 16%.Discharge content due in new discharge standard, calculating nitrogen oxides is based on oxygen-containing in the discharge gas What amount was calculated, therefore, while controlling the content of nitrogen oxides in gas, the oxygen content in the gas is suitably reduced, passed through Conversion is crossed, the content of nitrogen oxides in the discharge gas is also reduced.

In the present invention, the flue gas that down-draft drying zone is discharged is delivered to cold two sections of the air inlet of ring of ring cold machine, Since the temperature of the cold two sections of internal oxidition pelletizings of ring cold machine middle ring reaches 800~1000 DEG C, reduction is sprayed at cold two sections of the top of ring Agent, the flue gas being discharged from down-draft drying zone is after cold two sections of ring, and by heat exchange, temperature is increased to 800 DEG C or more, in ring cold two The top of section sprays into reducing agent, at this point, after reducing agent is mixed with flue gas, using the cold two sections of internal oxidition pelletizings of ring as reactive group Nitrogen oxides (NO in bed, reducing agent and flue gas_x) SNCR denitration reaction occurs, nitrogen is generated, to dispose in flue gas NO_x.In the prior art, it is directly arranged after desulfurization process and dust removal process from the flue gas that down-draft drying zone and preheated one-section are discharged It puts, the utility model changes this technology, this partial fume is delivered to cold two sections of ring, while spraying at cold two sections of the top of ring Reducing agent realizes SNCR denitration, reduces containing for nitrogen oxides in effluent using the hot environment of the cold two sections of internal oxidition pelletizings of ring Amount, it is then mixed with the flue gas of down-draft drying zone discharge in cold two sections of the ring flue gas recirculations by SNCR processing to preheated one-section After conjunction, a part therein is delivered to cold two sections of ring again, i.e., as cold two sections of the cooling wind of ring, and utilizes oxygen in cold two sections of ring Nitrogen oxides in the high-temperature process flue gas of pellet.The technique constantly recycles, the down-draft drying zone finally discharged from chimney Flue gas in, the content of nitrogen oxides can control in 100mg/Nm³Below.

The flue gas that down-draft drying zone is discharged can also be delivered to cold two sections of ring, using high temperature sinter in cold two sections of ring, The partial fume is heated, so that reaching 800 DEG C or more from the gas temperature of the cold two sections of discharges of ring, then by the part after heating Gas is handled by SNCR processing system, and SNCR denitration reaction occurs, and the nitrogen oxides in flue gas is reduced to nitrogen, reduces nitrogen The discharge of oxide.Meanwhile sinter of the partial fume as cooling gas, in the cold two sections of C2 of cooling ring.

In the present invention, by down-draft drying zone discharge flue gas (or in which a part, such as volume ratio be 10- 90%, preferably 20-80%, more preferably 30-70%) it is delivered to cold three sections of the air inlet of ring of ring cold machine, due to ring cold machine The temperature of the cold three sections of internal oxidition pelletizings of middle ring reaches 300~400 DEG C, sprays into reducing agent in the bellows of the cold three sections of bottoms of ring, also After former agent is mixed with flue gas, using the cold three sections of internal oxidition pelletizings of ring as reaction bedding, reducing agent and the nitrogen oxides in flue gas (NO_x) SCR denitration reaction occurs, nitrogen is generated, to dispose the NO in flue gas_x.In the prior art, from down-draft drying zone and The flue gas of preheated one-section discharge direct emission, the utility model after desulfurization process and dust removal process change this technology, will A part in this partial fume is delivered to cold three sections of ring, while spraying into reducing agent, utilizes the height of the cold three sections of internal oxidition pelletizings of ring Warm environment realizes SCR denitration, reduces the content of nitrogen oxides in effluent.In cold three sections of ring, by SCR, treated that flue gas follows again For ring to blasting drying period, treated, and flue gas had not only been used as cold three sections of the cooling wind of ring, but also utilized the cold three sections of internal oxidition pelletizings of ring Nitrogen oxides in high-temperature process flue gas.The technique constantly recycles, and further reduces from the flue gas that down-draft drying zone is discharged The content of nitrogen oxides, simultaneously as be delivered to cold three sections of the flue gas of ring have passed through SCR processing in cold three sections of ring, by drum After wind dryer section, the content of the nitrogen oxides in effluent of discharge is lower than 50mg/Nm³Below.

Can also by the flue gas being discharged from down-draft drying zone (or in which a part, such as volume ratio be 10-90%, it is excellent It is selected as 20-80%, more preferably 30-70%) it is further transported to as cooling wind: cold three sections of the air inlet of ring；Utilize ring High temperature sinter in cold three sections heats the portion gas, by the gas after the cold three sections of C3 heating of ring using SCR denitration system System processing, realizes SCR denitration.Meanwhile sinter of the partial fume as cooling gas, in the cold three sections of C3 of cooling ring.

In the present invention, it is further transported to using the gas being discharged from preheated one-section as cooling wind: ring cold one The air inlet of section.The exhaust gas volumn of circulation is adjusted in real time by autocontrol valve, the principle of adjusting: cold one section by on-line checking ring Oxygen content into rotary kiln hot wind, and when range of the oxygen content in 16-21% (preferably 17-20%, it is further excellent It is selected as 18-19%) (under the premise of not influencing yield and quality index), then amount of circulating gas adjustable range is 10~30% (by producing Institute's required airflow determines)；When oxygen content is 16-21% in flue gas (preferably 16-20%, further preferably 16-19%, More preferably 16-18%), then flue gas recirculation amount is reduced on aforementioned base, is entered in rotary kiln hot wind until cold one section of ring Oxygen content reaches 16-21% (preferably 17-21%, further preferably 18-21%, more preferably 19-21%).In technique Effect are as follows: 1, using the waste heat of flue gas, the temperature of the cold one section of hot wind of ring can be improved, flame temperature while reducing fuel consumption Degree can reduce, and the NOx that roasting process generates is reduced；2, cold one section of ring is back to using the flue gas recirculation compared with low oxygen content to be used as back The combustion air of rotary kiln central burner, due to the decline of oxygen content, thermal NO x is substantially reduced while reducing flame temperature, This technical measures can largely inhibit the generation of NOx, can also the oxygen content appropriate that reduced in flue gas.

In the present invention, the technique by by the high gas of oxygen content (in the prior art by the portion gas with contain Have direct emission after the gas mixing of nitrogen oxides) it is recycled to cold one section of ring, then it is delivered to rotary kiln, by ignition, from And the oxygen in the portion gas is consumed, the oxygen content in discharge gas is reduced, to further reduce in discharge gas The content of nitrogen oxides.

Preferably, the merging flue gas W that the utility model may be implemented to be discharged from down-draft drying zone DDD is as cold But wind is fully assigned the cold two sections of C2 of ring and the cold three sections of C3 of ring as cooling wind, and the flue gas of preheated one-section TPH discharge is delivered to The cold one section of C1 of ring is as cooling wind.The flue gas for being recycled to the cold one section of C1 of ring is delivered to again in rotary kiln 2, as combustion-supporting gas；It follows Ring is reacted with reducing agent to the flue gas of the cold two sections of C2 of ring and the cold three sections of C3 of ring, passes through SNCR denitration and SCR denitration reaction respectively, Remove the nitrogen oxides in flue gas.Using this technique, down-draft drying zone DDD and preheated one-section TPH zero-emission are realized.Only ring is cold Three sections of clean flue gases after treatment discharge after blasting drying period, in the flue gas of blasting drying period discharge, nitrogen oxides Content and clean air it is close, minimum discharge may be implemented in this technique, and the nitrogen oxides in the flue gas of generation may be implemented 99% removing.Amount of nitrogen oxides in the gas of the cold four sections of discharges of ring is lower, can be ignored completely.Flue gas is circulated throughout Cheng Zhong, if oxygen is not enough to normally roast in rotary kiln, only need in rotary kiln different oxygen-enriched gas or liquid oxygen, ring The extremely friendly production technology in border.

In the present invention, two sections of preheating of drying grate are delivered to from the hot wind that rotary kiln discharges, in two sections of preheating, Position above green-ball sprays into reducing agent, and reducing agent is reacted with the NOx entered in the hot wind for preheating two sections, realizes that SNCR is de- Nitre.The technical program will turn round the flue gas that roasting in kilns generates and preheating two using green-ball in two sections of preheating as reaction bedding Section carries out heat exchange with green-ball, while preheating green-ball, sprays into reducing agent, so that the nitrogen oxides in reducing agent and flue gas carries out SNCR denitration reaction, since the flue gas discharged from rotary kiln is directly entered two sections of preheating, this flue-gas temperature is higher, generally 800- 1100 DEG C, in the prior art using the green-ball in the smoke pre-heating drying grate, the utility model is preheating two sections of penetrating reducing agents, While carrying out heat exchange using the flue gas and green-ball, the nitrogen oxides in flue gas is handled, to reduce nitrogen oxidation in flue gas The content of object.

In the preferred embodiment of the utility model, preheating two sections in green-ball carry out heat exchange after hot wind using SCR processing system, reducing agent are reacted with from the NOx in two sections of hot winds for entering down-draft drying zone of preheating, realize SCR denitration.This Still higher feature makes partial fume progress SCR denitration reaction to flue-gas temperature of the technical solution after two sections of preheating The nitrogen oxides obtained in the reducing agent and flue gas in SCR processing system carries out SCR denitration reaction, due to after two sections of preheating Flue-gas temperature still has 300-450 DEG C or so, which is suitble to the SCR denitration reaction of nitrogen oxides.It in the prior art will input Flue gas and green-ball carry out direct emission after heat exchange in down-draft drying zone, cause the nitrogen oxides in effluent of discharge higher according to quantity, Do not conform to and accords with new discharge standard.

In the present invention, it is also provided with SCR denitration reaction device on the conveyance conduit for preheating two sections of discharge gas, adopted With the technique and system of the application, even if escaping out partial reduction activator from two sections of preheating, the partial reduction activation of escape Agent enters SCR processing system with flue gas, which continues the work for being catalyzed and restoring in SCR processing system With progress SCR reaction, consumes the reduction activator of escape, further improve reduction activator in SCR processing system Utilization rate also ensures production safety.

SCR processing system, mesh is arranged in the utility model on preheating two sections of setting reducing agent jetting devices and conveyance conduit First is that flue gas discharge by two procedures to rotary kiln carries out denitration process, the nitrogen oxidation in removing flue gas to greatest extent Object lowers the content that flue gas emission goes out nitrogen oxides；Purpose is second is that the reducing agent due to use is readily volatilized, if only pre- All there is the volatilization of a part in hot two sections of penetrating reduction activators, reducing agent therein, the reducing agent for escape of volatilizing is with flue gas Into down-draft drying zone, if the reducing agent escaped out that volatilizees just will directly arrange Xiang great Qi, greatly without being further processed Pollute environment.The utility model adds SCR denitration reaction process and device on conveyance conduit, so that the reducing agent escaped out exists It is consumed in SCR processing system, and generates the effect of denitration, make full use of the reducing agent, while avoiding the outlet of reducing agent.

In the present invention, it is equipped with residual heat using device, makes full use of and carries out heat exchange with green-ball in two sections of preheating The higher spy of temperature for the gas that tri- sections of discharge gas, the gas of bis- sections of air outlets of Cong Huanleng discharge, Cong Huanleng air outlets are discharged Point makes full use of residual heat resources, while adjusting the temperature of each section of discharge gas, reach optimum SNCR denitration reaction or SCR denitration reaction temperature improves denitration efficiency.

Still there is the gas being discharged from two sections of PH of preheating 500 DEG C or so of temperature to be received using the heat of the portion gas Collect and utilize waste heat；Such as: spray into the waste water that acid-making process (or other techniques) generate, by waste water by after atomizer with the portion Divide gas mixing；First, waste water can be reduced the temperature of portion gas, in the range of so that its temperature is reached 200-400 DEG C, this Temperature range is optimum SCR denitration temperature, improves denitration efficiency；Second, this processing mode can solve waste water and be difficult to handle The problem of, waste water is sprayed into flue gas, then by being handled by SCR, waste water is handled together.From the cold two sections of C2 air outlets of ring The temperature of the gas of discharge be 1200 DEG C or more, by the portion gas by being exchanged heat with heat exchanger after, reduce the part gas For the temperature of body to 800-1000 DEG C or so, which is the temperature of optimum SNCR denitration reaction, improves denitration efficiency；Meanwhile The heat that the portion gas is collected by heat exchanger can be used for pneumatic conveying, take off other purposes such as white.Go out from the cold three sections of C3 of ring Air port discharge gas temperature be 350 DEG C or so, by the portion gas by being exchanged heat with heat exchanger after, reduce the part For the temperature of gas to 250 DEG C or so, which is the temperature for being suitable for SNCR denitration reaction, improves denitration efficiency；Meanwhile by changing Hot device collects the heat of the portion gas, can be used for pneumatic conveying, takes off other purposes such as white.

In the present invention, it is discharged by cold four sections gases discharged after exchanging heat of ring, after blasting drying period exchanges heat Gas, down-draft drying zone and the portion gas of preheated one-section discharge for pneumatic conveying or taking off white.It in the prior art, will be above-mentioned The gas of position discharge directly arranges Xiang great Qi.Waste heat in the gas of the above-mentioned position discharge of this technology utilization, more than the part Heat is for pneumatic conveying or takes off the purposes such as white, gives full play to the value of UTILIZATION OF VESIDUAL HEAT IN, saves the energy, reduces the pollution to environment.

In the present invention, reducing agent mainly (such as NaCl, is contained by ammonia agent (such as ammonium hydroxide, urea reducing agent) and auxiliary agent Vanadium solution, mesoporous/micropore nanophase materials etc.) composition, reduction activator dosage is according to NO in flue gas_xConcentration adjust.

In the present invention, SNCR denitration reaction temperature is 600-1100 DEG C, and preferably 700-1000 DEG C, more preferably It is 800-950 DEG C.SCR denitration reaction temperature is 200-500 DEG C, preferably 250-450 DEG C, more preferably 300-400 DEG C.

In the technical solution of the utility model, realize that the oxygen content in discharge flue gas subtracts significantly by multiple technological means It is small, while the total emission volumn of nitrogen oxides and concentration greatly reduce.Wherein, to be delivered to ring cold for flue gas preheated one-section being discharged It one section, then enters back into rotary kiln and burns, middle cold one section of idle loop of cold air is delivered to the partial fume compared with the existing technology Gas temperature in rotary kiln is higher, convenient for the heating in rotary kiln, reduces the use of fuel, while reducing in rotary kiln and roasting It makes a fire the temperature of flame, to reduce the generation of NOx from source.Furthermore it is cold that the flue gas that down-draft drying zone is discharged is delivered to ring Two sections by SNCR denitrations handle, using cold two sections of the hot environment of ring, at the same using the acid pellet in cold two sections of ring as Bedding is reacted, the nitrogen oxides in the flue gas generated is removed.Equally, to be delivered to ring cold for flue gas down-draft drying zone discharged Three sections are handled by SCR denitration, using cold three sections of the hot environment of ring, while using the acid pellet in cold three sections of ring as anti- Bedding is answered, the nitrogen oxides in the flue gas generated is removed.

The art of this patent is equally applicable to pelletizing belt type roasting machine and other Pelletizing Process with the technical characterstic.

In this application, the length of drying grate be 10-150 meters, preferably 20-80 meters, preferably 30-70 meters, more preferably It is 40-60 meters.The length of rotary kiln is usually 20-60 meters, and preferably 25-50 meters, more preferably 30-45 meters, such as 35 or 40 Rice.

Compared with prior art, the technical solution of the utility model has following advantageous effects:

1, using high temperature sinter in cold two sections of ring, make from down-draft drying zone be discharged flue gas directly in cold two sections of ring into The reaction of row SNCR denitration；Or the flue gas being discharged from down-draft drying zone is heated using high temperature sinter in cold two sections of ring, then will The portion gas after heating is handled by SNCR processing system, and SNCR denitration reaction occurs, reduce nitrogen oxides concentration and Content；

2, using high temperature sinter in cold three sections of ring, make from down-draft drying zone be discharged flue gas directly in cold three sections of ring into Row SCR denitration reaction；Or the flue gas being discharged from down-draft drying zone is heated using high temperature sinter in cold three sections of ring, then it will add The portion gas after heat is handled by SCR processing system, and SCR denitration reaction occurs, reduces the concentration and content of nitrogen oxides；

3, cold one section of ring is further transported to using the gas being discharged from preheated one-section as cooling wind, more than flue gas The temperature of the cold one section of hot wind of ring can be improved in heat, and flame temperature can reduce while reducing fuel consumption, and roasting process generates NOx reduce.

4, it is equipped with residual heat using device, makes full use of and carries out heat exchange discharge gas with green-ball in two sections of preheating, from ring The higher feature of temperature for the gas that tri- sections of gas, the Cong Huanleng air outlets of cold two sections of air outlets discharge are discharged, makes full use of remaining Thermal resource, while the temperature of each section of discharge gas is adjusted, reach the reaction of optimum SNCR denitration or SCR denitration reaction temperature Degree improves denitration efficiency.

Detailed description of the invention

Fig. 1 is a kind of flow chart of the production technology of pelletizing flue gas ultra-low NOx emission of the utility model；

Fig. 2 is flue gas conveying in down-draft drying zone in a kind of production technology of pelletizing flue gas ultra-low NOx emission of the utility model To cold two sections of ring and cold three sections of the process flow chart of ring；

Fig. 3 is a kind of cold two sections of progress SNCR, ring of production technology middle ring of pelletizing flue gas ultra-low NOx emission of the utility model The process flow chart of cold three sections of progress SCR；

Fig. 4 is that preheated one-section gas conveys word in a kind of production technology of pelletizing flue gas ultra-low NOx emission of the utility model Cold one section of the process flow chart of ring；

Fig. 5 is a kind of technique whole process figure of the production technology of pelletizing flue gas ultra-low NOx emission of the utility model；

Fig. 6 is a kind of structural schematic diagram of the production system of pelletizing flue gas ultra-low NOx emission of the utility model；

Fig. 7 is that a kind of another design structure of production system of pelletizing flue gas ultra-low NOx emission of the utility model is illustrated Figure；

Fig. 8 is the knot that SCR processing system is equipped in a kind of production system of pelletizing flue gas ultra-low NOx emission of the utility model Structure schematic diagram；

Fig. 9 is that residual heat using device is equipped in a kind of production system of pelletizing flue gas ultra-low NOx emission of the utility model Structural schematic diagram；

Figure 10 is each device feature discharge gas in a kind of production system of pelletizing flue gas ultra-low NOx emission of the utility model Guiding figure.

Appended drawing reference:

1: drying grate；UDD: blasting drying period；DDD: down-draft drying zone；TPH: preheated one-section；PH: two sections of preheating；2: returning Rotary kiln；201: the air inlet of rotary kiln；202: the air outlet of rotary kiln；C: ring cold machine；C1: cold one section of ring；C1a: cold one section of ring Air inlet；C1b: cold one section of the air outlet of ring；C2: cold two sections of ring；C2a: cold two sections of the air inlet of ring；C2b: cold two sections of ring Air outlet；C3: cold three sections of ring；C3a: cold three sections of the air inlet of ring；C3b: cold three sections of the air outlet of ring；C4: cold four sections of ring；C4b: Cold four sections of the air outlet of ring；301: the air inlet of two sections of preheating；302: the air outlet of two sections of preheating；303: the air inlet of preheated one-section Mouthful；304: the air outlet of preheated one-section；305: the air inlet of down-draft drying zone；306: the air outlet of down-draft drying zone；307: drum The air inlet of wind dryer section；308: the air outlet of blasting drying period；401: the first reducing agent jetting devices；402: the second reducing agents Jetting device；403: third reducing agent jetting device；5:SNCR processing system；601: the one SCR processing systems；602: the second SCR processing system；701: the first dust-extraction units；702: the second dust-extraction units；703: third dust-extraction unit；801: the first desulfurization dress It sets；802: the second desulfurizers；901: the first residual heat using devices；902: the second residual heat using devices；903: third waste heat benefit Use device；10: blower；11: chimney；L1: first pipe；L2: second pipe；L3: third pipeline；L4: the four pipeline；L5: the Five pipelines；L6: the six pipeline；L7: the seven pipeline；L8: the eight pipeline；L9: the nine pipeline；L10: the ten pipeline；L11: the ten One pipeline；L12: the ten two pipeline.

Specific embodiment

According to embodiment provided by the utility model, a kind of production system of pelletizing flue gas ultra-low NOx emission is provided.

A kind of production system of pelletizing flue gas ultra-low NOx emission, the system include: drying grate 1, rotary kiln 2, ring cold machine C. Wherein: being moved towards according to technique, the drying grate 1 is disposed with blasting drying period UDD, down-draft drying zone DDD, preheated one-section Two sections of PH of TPH and preheating.Ring cold machine C is disposed with the cold one section of C1 of ring, the cold two sections of C2 of ring, the cold three sections of C3 of ring and cold four sections of ring C4.The cold one section of C1 of ring that two sections of PH of preheating of the tail end connection drying grate 1 of rotary kiln 2 connect ring cold machine C with the other end.

Wherein: the air outlet C1b of the cold one section of C1 of ring is connected to the air inlet 201 of rotary kiln 2 via first pipe L1, revolution The air outlet 202 of kiln 2 is connected to the air inlet 301 of two sections of PH of preheating via second pipe L2, preheats the air outlet 302 of two sections of PH The air inlet 305 of down-draft drying zone DDD is connected to by third pipeline L3.

The air outlet C2b of the cold two sections of C2 of ring is connected to the air inlet 303 of preheated one-section TPH via the 4th pipeline L4；Ring is cold The air outlet C3b of three sections of C3 is connected to the air inlet 307 of blasting drying period UDD via the 5th pipeline L5.

Wherein: the air outlet 306 of down-draft drying zone DDD is connected to the air inlet of the cold two sections of C2 of ring via the 6th pipeline L6 C2a；Simultaneously:

It is equipped with the first reducing agent jetting device 401 positioned at the top of the cold two sections of C2 of ring, alternatively, the 4th pipeline L4 is equipped with SNCR processing system 5.

Preferably, it is the 7th pipeline L7 that the 6th pipeline L6, which separates one article of branch,.7th pipeline L7 is connected to cold three sections of ring The air inlet C3a of C3；Simultaneously:

It is equipped with the second reducing agent jetting device 402 positioned at the position of cold three sections of bottoms the C3 bellows of ring, alternatively, the 5th pipeline L5 It is equipped with the first SCR processing system 601.

Preferably, the air outlet 304 of preheated one-section TPH is connected to the air inlet of the cold one section of C1 of ring via the 8th pipeline L8 C1a。

Preferably, being equipped with third reducing agent jetting device 403 positioned at the top of green-ball charge level in two sections of PH of preheating.

Preferably, third pipeline L3 is equipped with the 2nd SCR processing system 602.

Preferably, be additionally provided with the first dust-extraction unit 701 on third pipeline L3, and the first dust-extraction unit 701 is located at the The upstream of two SCR processing systems 602.

Preferably, the 6th pipeline L6 is equipped with the second dust-extraction unit 702 and the first desulfurizer 801, and second removes The upstream for separating the 7th position pipeline L7 is arranged in dirt device 702 and the first desulfurizer 801.

Preferably, the 8th pipeline L8 is equipped with third dust-extraction unit 703 and the second desulfurizer 802.

Preferably, third pipeline L3 is equipped with the first residual heat using device 901, and the first residual heat using device 901 It is arranged between the first dust-extraction unit 701 and the 2nd SCR processing system 602.

Preferably, the 4th pipeline L4 is equipped with the second residual heat using device 902, and the second residual heat using device 902 The upstream of SNCR processing system 5 is set.

Preferably, the 5th pipeline L5 is equipped with third residual heat using device 903, and third residual heat using device 903 The upstream of first SCR processing system 601 is set.

In the present invention, the first residual heat using device 901, the second residual heat using device 902, third UTILIZATION OF VESIDUAL HEAT IN dress It sets 903 and independently respectively solely is heat exchanger or wastewater treatment equipment.

In the present invention, the cold one section of C1 of ring, the cold two sections of C2 of ring, the cold three sections of C3 of ring and the air inlet of the cold four sections of bottoms C4 of ring Mouth is connect with blower 10.

In the present invention, the air outlet C4b of the cold four sections of C4 of ring is connect with the 9th pipeline L9.9th pipeline L9 is connected to Chimney 10.

In the present invention, the air outlet 308 of blasting drying period UDD is connect with the tenth pipeline L10.Tenth pipeline L10 It is connected to chimney 11.

Preferably, the Article 2 branch that the 6th pipeline L6 is separated is the 11st pipeline L11.8th pipeline L8 separate one Article branch is the 12nd pipeline L12.11st pipeline L11 and the 12nd pipeline L12 are connected to chimney 11.

Preferably, the 11st pipeline L11, the 12nd pipeline L12, the 9th pipeline L9, the part in the tenth pipeline L10 or Chimney 11 is connected to after all merging.

In the present invention, the length of drying grate is 10-150 meters.

Embodiment 1

As shown in fig. 6, a kind of production system of pelletizing flue gas ultra-low NOx emission, the system include: drying grate 1, rotary kiln 2, ring cold machine C.Wherein: moved towards according to technique, the drying grate 1 be disposed with blasting drying period UDD, down-draft drying zone DDD, Two sections of PH of preheated one-section TPH and preheating.Ring cold machine C is disposed with the cold one section of C1 of ring, the cold two sections of C2 of ring, the cold three sections of C3 of ring and ring Cold four sections of C4.The cold one section of C1 of ring that two sections of PH of preheating of the tail end connection drying grate 1 of rotary kiln 2 connect ring cold machine C with the other end.

Wherein: the air outlet 306 of down-draft drying zone DDD is connected to the air inlet of the cold two sections of C2 of ring via the 6th pipeline L6 C2a；Simultaneously: being equipped with the first reducing agent jetting device 401 positioned at the top of the cold two sections of C2 of ring；The length of drying grate is 40 meters.

Embodiment 2

Wherein: the air outlet 306 of down-draft drying zone DDD is connected to the air inlet of the cold two sections of C2 of ring via the 6th pipeline L6 C2a；Simultaneously: the 4th pipeline L4 is equipped with SNCR processing system 5；The length of drying grate is 80 meters.

Embodiment 3

As shown in fig. 7, repeating embodiment 1, it is the 7th pipeline L7 that only the 6th pipeline L6, which separates one article of branch,.7th pipeline L7 is connected to the air inlet C3a of the cold three sections of C3 of ring；Simultaneously: being equipped with the second reducing agent positioned at the position of cold three sections of bottoms the C3 bellows of ring Jetting device 402.

Embodiment 4

As shown in fig. 7, repeating embodiment 2, it is the 7th pipeline L7 that only the 6th pipeline L6, which separates one article of branch,.7th pipeline L7 is connected to the air inlet C3a of the cold three sections of C3 of ring；Simultaneously: the 5th pipeline L5 is equipped with the first SCR processing system 601.

Embodiment 5

As shown in figure 8, repeating embodiment 3, only the air outlet 304 of preheated one-section TPH is connected to via the 8th pipeline L8 The air inlet C1a of the cold one section of C1 of ring.

Embodiment 6

Embodiment 5 is repeated, is only preheated in two sections of PH, is equipped with third reducing agent jetting device positioned at the top of green-ball charge level 403.Third pipeline L3 is equipped with the 2nd SCR processing system 602.The first dust-extraction unit 701 is additionally provided on third pipeline L3, and First dust-extraction unit 701 is located at the upstream of the 2nd SCR processing system 602.

Embodiment 7

Embodiment 6 is repeated, only the 6th pipeline L6 is equipped with the second dust-extraction unit 702 and the first desulfurizer 801, and The upstream for separating the 7th position pipeline L7 is arranged in second dust-extraction unit 702 and the first desulfurizer 801.It is set on 8th pipeline L8 There are third dust-extraction unit 703 and the second desulfurizer 802.

Embodiment 8

As shown in figure 9, repeating embodiment 7, only third pipeline L3 is equipped with the first residual heat using device 901, and the One residual heat using device 901 is arranged between the first dust-extraction unit 701 and the 2nd SCR processing system 602.It is set on 4th pipeline L4 There is the second residual heat using device 902, and the upstream of SNCR processing system 5 is arranged in the second residual heat using device 902.5th pipe Road L5 is equipped with third residual heat using device 903, and third residual heat using device 903 is arranged in the first SCR processing system 601 Upstream.First residual heat using device 901 is wastewater treatment equipment, and wastewater treatment equipment includes gas access, gas vent, gives up Water inlet, atomizer.903 pipe heat exchanger of second residual heat using device 902 and third residual heat using device.

Embodiment 9

As shown in Figure 10, embodiment 8 is repeated, only the cold one section of C1 of ring, the cold two sections of C2 of ring, the cold three sections of C3 of ring and cold four sections of ring The air inlet of the bottom C4 is connect with blower 10.The air outlet C4b of the cold four sections of C4 of ring is connect with the 9th pipeline L9, blasting drying period The air outlet 308 of UDD is connect with the tenth pipeline L10, and the Article 2 branch that the 6th pipeline L6 is separated is the 11st pipeline L11, the One article of branch that eight pipeline L8 are separated is the 12nd pipeline L12；11st pipeline L11 is connected to after merging with the 9th pipeline L9 Chimney 11；12nd pipeline L12 is connected to chimney 11 after merging with the tenth pipeline L10.

Embodiment 10

As shown in Figure 1, a kind of production technology of pelletizing flue gas ultra-low NOx emission, the production technology the following steps are included:

1) green-ball is on drying grate 1 successively by blasting drying period UDD, down-draft drying zone DDD, preheated one-section TPH and pre- Two sections of PH of heat are dried, preheat, and roast subsequently into passing through in rotary kiln 2, then successively pass through cold one section of ring on ring cold machine C The cold two sections of C2 of C1, ring, the cold three sections of C3 of ring and the cold four sections of C4 of ring are cooled down, and acid pellet is obtained；

2) it is increased by the cooling wind temperature of the cold one section of C1 of ring, the wind of the cold one section of C1 discharge of ring is delivered in rotary kiln 2 Pellet roasting is participated in, the hot wind discharged from rotary kiln 2 is delivered to two sections of PH of preheating of drying grate 1；The hot wind is preheating two sections of PH Down-draft drying zone DDD is delivered to after the interior progress heat exchange with green-ball；

3) it is increased by the cooling wind temperature of the cold two sections of C2 of ring, the wind of the cold two sections of C2 discharge of ring is delivered to drying grate 1 Preheated one-section TPH, and heat exchange is carried out with green-ball in preheated one-section TPH, preheat green-ball；

4) it is increased by the cooling wind temperature of the cold three sections of C3 of ring, the wind of the cold three sections of C3 discharge of ring is delivered to drying grate 1 Blasting drying period UDD, and heat exchange is carried out with green-ball in blasting drying period UDD, then from the exhaust outlet of blasting drying period UDD Discharge；

Wherein: from down-draft drying zone DDD be discharged flue gas be further transported to as cooling wind: the cold two sections of C2 of ring into Air port；Simultaneously: in the flue gas positioned at the top of the cold two sections of C2 of ring penetrating reducing agent, reducing agent and after the cold two sections of C2 of ring NO_xSNCR denitration is realized in reaction.

Using this technique, the DDD flue gas being discharged in down-draft drying zone is delivered to the cold two sections of C2 of ring, sprays into reducing agent, is utilized High temperature sinter in the cold two sections of C2 of ring, using high temperature sinter as reaction bedding, so that nitrogen oxides and penetrating in flue gas SNCR denitration reaction occurs in the cold two sections of C2 of ring for reducing agent, and the nitrogen oxides in flue gas is reduced to nitrogen, reduces nitrogen oxidation The discharge of object.Meanwhile sinter of the partial fume as cooling gas, in the cold two sections of C2 of cooling ring.By the process Afterwards, from the flue gas of smoke stack emission, NO_xContent is 79.3mg/Nm³。

Embodiment 11

As shown in figure 3, a kind of production technology of pelletizing flue gas ultra-low NOx emission, the production technology the following steps are included:

Wherein: from down-draft drying zone DDD be discharged flue gas be further transported to as cooling wind: the cold two sections of C2 of ring into Air port；Simultaneously: the gas of bis- sections of C2 air outlets of Cong Huanleng discharge is delivered to the preheating of drying grate 1 again after SNCR processing system One section of TPH.

Using this technique, the DDD flue gas being discharged in down-draft drying zone is delivered to the cold two sections of C2 of ring, using in the cold two sections of C2 of ring High temperature sinter heats the partial fume, so that reaching 800 DEG C or more from the gas temperature that the cold two sections of C2 of ring are discharged, then will The portion gas after heating is handled by SNCR processing system, SNCR denitration reaction occurs, also by the nitrogen oxides in flue gas Originally it is nitrogen, reduces the discharge of nitrogen oxides.Meanwhile burning of the partial fume as cooling gas, in the cold two sections of C2 of cooling ring Tie mine.After the process, from the flue gas of smoke stack emission, NO_xContent is 76.1mg/Nm³。

Embodiment 12

As shown in Fig. 2, embodiment 10 is repeated, 70% (volume ratio) in the flue gas that only down-draft drying zone DDD is discharged The cold two sections of C2 of ring are delivered to, reducing agent are sprayed into, using high temperature sinter in the cold two sections of C2 of ring, using high temperature sinter as reactive group Bed, so that SNCR denitration reaction occurs in the cold two sections of C2 of ring for the reducing agent of nitrogen oxides and penetrating in flue gas, it will be in flue gas Nitrogen oxides be reduced to nitrogen, reduce the discharge of nitrogen oxides.Meanwhile the partial fume, as cooling gas, cooling ring is cold Sinter in two sections of C2.

30% (volume ratio) of the flue gas being discharged from down-draft drying zone DDD is further transported to as cooling wind: ring is cold The air inlet of three sections of C3；Simultaneously: spraying into reducing agent in the position for being located at cold three sections of bottoms the C3 bellows of ring, reducing agent is done with from exhausting NO in the flue gas of dry section of DDD discharge_xSCR denitration is realized in reaction.Meanwhile the partial fume, as cooling gas, cooling ring is cold Sinter in three sections of C3.

The DDD flue gas being discharged in down-draft drying zone is divided into two parts by this technique, de- by SNCR in the cold two sections of C2 of ring respectively Nitre reaction, passes through SCR denitration reaction in the cold three sections of C3 of ring；Improve out of stock efficiency.After the process, from smoke stack emission Flue gas in, NO_xContent is 78.5mg/Nm³。

Embodiment 13

Embodiment 11 is repeated, it is cold that 70% (volume ratio) in flue gas that down-draft drying zone DDD is discharged only is delivered to ring Two sections of C2 heat the partial fume using high temperature sinter in the cold two sections of C2 of ring, so that the gas temperature being discharged from the cold two sections of C2 of ring Degree reaches 800 DEG C or more, then handles the portion gas after heating by SNCR processing system, it is anti-that SNCR denitration occurs It answers, the nitrogen oxides in flue gas is reduced to nitrogen, reduces the discharge of nitrogen oxides.Meanwhile the partial fume is as cooling air Body, the sinter in the cold two sections of C2 of cooling ring.

30% (volume ratio) of the flue gas being discharged from down-draft drying zone DDD is further transported to as cooling wind: ring is cold The air inlet of three sections of C3；Simultaneously: the gas of the cold three sections of C3 air outlets discharge of ring is delivered to drying grate after SCR processing system again 1 blasting drying period UDD.Meanwhile sinter of the partial fume as cooling gas, in the cold three sections of C3 of cooling ring.

The DDD flue gas being discharged in down-draft drying zone is divided into two parts by this technique, respectively after through the cold two sections of C2 heating of ring It is handled by SNCR denitration system processing, after three section C3 cold by ring heating by SCR denitration system, improves out of stock efficiency. After the process, from the flue gas of smoke stack emission, NO_xContent is 73.4mg/Nm³。

Embodiment 14

As shown in figure 4, repeating embodiment 12, the only technique further include: the gas that step 6) is discharged from preheated one-section TPH It is further transported to as cooling wind: the air inlet of the cold one section of C1 of ring.

The high gas of oxygen content (portion gas and will be contained the gas mixing of nitrogen oxides in the prior art by the technique Direct emission afterwards) it is recycled to the cold one section of C1 of ring, then it is delivered to rotary kiln, by ignition, to consume the portion gas In oxygen, reduce discharge gas in oxygen content, to further reduce the content of nitrogen oxides in discharge gas.By It is 16% calculating, NO based on benchmark oxygen content from the flue gas of smoke stack emission after the process_xContent is 53.2mg/Nm³。

Embodiment 15

As shown in figure 4, repeating embodiment 13, only technique further include: the gas work that step 6) be discharged from preheated one-section TPH It is further transported to for cooling wind: the air inlet of the cold one section of C1 of ring.

The high gas of oxygen content (portion gas and will be contained the gas mixing of nitrogen oxides in the prior art by the technique Direct emission afterwards) it is recycled to the cold one section of C1 of ring, then it is delivered to rotary kiln, by ignition, to consume the portion gas In oxygen, reduce discharge gas in oxygen content, to further reduce the content of nitrogen oxides in discharge gas.By It is 16% calculating, NO based on benchmark oxygen content from the flue gas of smoke stack emission after the process_xContent is 50.7mg/Nm³。

Embodiment 16

Repeat embodiment 14, only preheating in two sections of PH, position above green-ball sprays into reducing agent, reducing agent with Into NO contained in the hot wind in two sections of PH of preheating_xSNCR denitration is realized in reaction.Hot wind preheat two sections of PH in and green-ball into After row heat exchange, the gas of discharge by dust removal process and then carries out SCR processing, is then delivered to down-draft drying zone again DDD。

In the prior art, which generates NO_xMain positions be rotary kiln, the flue gas in rotary kiln is delivered to preheating two Section PH.The high temperature feature of the flue gas of two sections of PH of technology utilization conveying preheating of the utility model, general temperature is 1000 DEG C of left sides The right side is appropriate for SNCR denitration reaction.Reducing agent is sprayed into preheating in two sections of PH, is using the green-ball mineral aggregate in two sections of PH of preheating React bedding, reducing agent and NO contained in the hot wind entered in two sections of PH of preheating_xSNCR denitration is realized in reaction.Then from pre- The gas of two sections of PH of heat discharge still has 500 DEG C or so of temperature, then the gas for preheating two sections of PH discharges is carried out SCR denitration Reaction, is further reduced the content and concentration of nitrogen oxides in effluent.After the process, from the flue gas of smoke stack emission In, it is 16% calculating, NO based on benchmark oxygen content_xContent is 48.7mg/Nm³。

Embodiment 17

Embodiment 16 is repeated, only hot wind is preheating in two sections of PH and after green-ball progress heat exchange, and the gas of discharge passes through After dust removal process, by wastewater treatment equipment, SCR processing is then carried out again.The gas being discharged from the cold two sections of C2 air outlets of ring By pipe heat exchanger, then using SNCR processing system, SNCR denitration is realized.The gas being discharged from the cold three sections of C3 air outlets of ring Body, then using SCR processing system, realizes SCR denitration by pipe heat exchanger.

In this technique, UTILIZATION OF VESIDUAL HEAT IN is carried out using the heat of flue gas.The gas being discharged from two sections of PH of preheating still has 500 DEG C or so temperature spray into the waste water that acid-making process (or other techniques) generate, waste water led to using the heat of the portion gas It is mixed after crossing atomizer with the portion gas；First, waste water can be reduced the temperature of portion gas, its temperature is made to reach 200- In the range of 400 DEG C, this temperature range is optimum SCR denitration temperature, improves denitration efficiency；Second, this processing mode can be with It solves the problems, such as that waste water is difficult to handle, waste water is sprayed into flue gas, then by being handled by SCR, waste water is handled together.From The temperature of the gas of the cold two sections of C2 air outlets discharge of ring is 1200 DEG C or more, by the portion gas by exchanging heat with heat exchanger Afterwards, the temperature of the portion gas is reduced to 1000 DEG C or so, which is the temperature of optimum SNCR denitration reaction, improves denitration Efficiency；Meanwhile the heat of the portion gas is collected by heat exchanger, it can be used for pneumatic conveying, take off other purposes such as white.From ring The temperature of the gas of cold three sections of C3 air outlets discharge is 350 DEG C or so, by the portion gas by being exchanged heat with heat exchanger after, The temperature of the portion gas is reduced to 250 DEG C or so, which is the temperature for being suitable for SNCR denitration reaction, improves denitration efficiency； Meanwhile the heat of the portion gas is collected by heat exchanger, it can be used for pneumatic conveying, take off other purposes such as white.

Embodiment 18

As shown in figure 5, repeat embodiment 17, the gas that is discharged after ring cold four sections of C4 heat exchange, by blasting drying period The portion gas of gas, down-draft drying zone DDD and the preheated one-section TPH discharge discharged after UDD heat exchange is for pneumatic conveying or takes off It is white.

In the prior art, the gas that above-mentioned position is discharged directly is arranged into Xiang great Qi.The above-mentioned position discharge of this technology utilization Waste heat in gas for pneumatic conveying or takes off the purposes such as white using the part of waste heat, gives full play to the value of UTILIZATION OF VESIDUAL HEAT IN, saves The energy is saved, the pollution to environment is reduced.

Claims

1. a kind of production system of pelletizing flue gas ultra-low NOx emission, which includes: drying grate (1), rotary kiln (2), ring cold machine (C)；Wherein: moved towards according to technique, the drying grate (1) be disposed with blasting drying period (UDD), down-draft drying zone (DDD), Two sections (PH) of preheated one-section (TPH) and preheating, it is cold that ring cold machine (C) is disposed with ring cold one section (C1), ring cold two sections of (C2), rings Two sections of preheating (PH) of three sections of tetra- sections of (C3) Ji Huanleng (C4), tail end connection drying grate (1) of rotary kiln (2) are connected with the other end The ring of ring cold machine (C) is cold one section (C1)；

Wherein: the air outlet (C1b) of ring cold one section (C1) is connected to the air inlet of rotary kiln (2) via first pipe (L1) (201), the air outlet (202) of rotary kiln (2) is connected to the air inlet (301) of preheating two sections (PH) via second pipe (L2), The air outlet (302) of preheating two sections (PH) is connected to the air inlet (305) of down-draft drying zone (DDD) by third pipeline (L3)；

The air outlet (C2b) of ring cold two sections (C2) is connected to the air inlet of preheated one-section (TPH) via the 4th pipeline (L4) (303)；The air outlet (C3b) of ring cold three sections (C3) is connected to the air inlet of blasting drying period (UDD) via the 5th pipeline (L5) (307)；

It is characterized by: via the 6th pipeline (L6) to be connected to ring cold two sections (C2) for the air outlet (306) of down-draft drying zone (DDD) Air inlet (C2a)；Simultaneously:

It is equipped with the first reducing agent jetting device (401) positioned at the top of ring cold two sections (C2), alternatively, the 4th pipeline (L4) is equipped with SNCR processing system (5)；

Wherein: the length of drying grate (1) is 10-150 meters.

2. production system according to claim 1, it is characterised in that: it is the 7th pipe that the 6th pipeline (L6), which separates one article of branch, Road (L7), the 7th pipeline (L7) are connected to the air inlet (C3a) of ring cold three sections (C3)；Simultaneously:

It is equipped with the second reducing agent jetting device (402) positioned at the position of cold three sections of bottoms (C3) bellows of ring, alternatively, the 5th pipeline (L5) it is equipped with the first SCR processing system (601).

3. production system according to claim 1 or 2, it is characterised in that: the air outlet (304) of preheated one-section (TPH) passes through The air inlet (C1a) of ring cold one section (C1) is connected to by the 8th pipeline (L8)；And/or

In two sections of preheating (PH), third reducing agent jetting device (403) is equipped with positioned at the top of green-ball charge level.

4. production system according to claim 3, it is characterised in that: third pipeline (L3) is equipped with the 2nd SCR processing system It unites (602)；And/or

6th pipeline (L6) is equipped with the second dust-extraction unit (702) and the first desulfurizer (801), and the second dust-extraction unit (702) it is arranged with the first desulfurizer (801) in the upstream for separating the 7th position pipeline (L7)；8th pipeline (L8) is equipped with the Three dust-extraction units (703) and the second desulfurizer (802).

5. production system according to claim 4, it is characterised in that: be additionally provided with the first dust-extraction unit on third pipeline (L3) (701), and the first dust-extraction unit (701) is located at the upstream of the 2nd SCR processing system (602).

6. production system according to claim 5, it is characterised in that: third pipeline (L3) is filled equipped with the first UTILIZATION OF VESIDUAL HEAT IN It sets (901), and the first residual heat using device (901) is arranged in the first dust-extraction unit (701) and the 2nd SCR processing system (602) between；And/or

4th pipeline (L4) is equipped with the second residual heat using device (902), and the second residual heat using device (902) setting exists The upstream of SNCR processing system (5)；And/or

5th pipeline (L5) is equipped with third residual heat using device (903), and third residual heat using device (903) setting is the The upstream of one SCR processing system (601).

7. production system according to claim 6, it is characterised in that: the first residual heat using device (901), the second waste heat benefit Heat exchanger or wastewater treatment equipment independently respectively solely are with device (902), third residual heat using device (903).

8. production system according to claim 7, it is characterised in that: heat exchanger is pipe heat exchanger；Wastewater treatment equipment Including gas access, gas vent, waterwater entrance, atomizer.

9. according to claim 1-2, production system described in any one of 4-8, it is characterised in that: ring cold one section of (C1), ring is cold Two sections (C2), the air inlet of the tetra- sections of bottoms (C4) cold three sections of (C3) Ji Huanleng of ring connect with blower (10)；And/or

The air outlet (C4b) of ring cold four sections (C4) is connect with the 9th pipeline (L9), and the 9th pipeline (L9) is connected to chimney (11)；Drum The air outlet (308) of wind dryer section (UDD) is connect with the tenth pipeline (L10), and the tenth pipeline (L10) is connected to chimney (11).

10. production system according to claim 3, it is characterised in that: ring cold one section (C1), ring cold two sections of (C2), rings are cold The air inlet of the tetra- sections of bottoms (C4) three sections of (C3) Ji Huanleng is connect with blower (10)；And/or

11. production system according to claim 9, it is characterised in that: the Article 2 branch that the 6th pipeline (L6) separates is 11st pipeline (L11), one article of branch that the 8th pipeline (L8) separates be the 12nd pipeline (L12), the 11st pipeline (L11) and 12nd pipeline (L12) is connected to chimney (11).

12. production system according to claim 10, it is characterised in that: the Article 2 branch that the 6th pipeline (L6) separates is 11st pipeline (L11), one article of branch that the 8th pipeline (L8) separates be the 12nd pipeline (L12), the 11st pipeline (L11) and 12nd pipeline (L12) is connected to chimney (11).

13. production system according to claim 11 or 12, it is characterised in that: the 11st pipeline (L11), the 12nd pipeline (L12), the 9th pipeline (L9), merge some or all of in the tenth pipeline (L10) after be connected to chimney (11).