CN104226110B - Coal-fired boiler SCR (Selective Catalytic Reduction) denitration control method and system - Google Patents

Coal-fired boiler SCR (Selective Catalytic Reduction) denitration control method and system Download PDF

Info

Publication number
CN104226110B
CN104226110B CN201410527517.6A CN201410527517A CN104226110B CN 104226110 B CN104226110 B CN 104226110B CN 201410527517 A CN201410527517 A CN 201410527517A CN 104226110 B CN104226110 B CN 104226110B
Authority
CN
China
Prior art keywords
ammonia
catalyst
mol ratio
coal
subregion
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN201410527517.6A
Other languages
Chinese (zh)
Other versions
CN104226110A (en
Inventor
谢慧
朱红涛
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
HENAN ZHONGHE ELECTRIC POWER TECHNOLOGY Co Ltd
Original Assignee
HENAN ZHONGHE ELECTRIC POWER TECHNOLOGY Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by HENAN ZHONGHE ELECTRIC POWER TECHNOLOGY Co Ltd filed Critical HENAN ZHONGHE ELECTRIC POWER TECHNOLOGY Co Ltd
Priority to CN201410527517.6A priority Critical patent/CN104226110B/en
Publication of CN104226110A publication Critical patent/CN104226110A/en
Application granted granted Critical
Publication of CN104226110B publication Critical patent/CN104226110B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Abstract

The invention relates to a coal-fired boiler SCR denitration control method and system. The method includes the steps of monitoring the molar ratio of ammonia and nitrogen in each section in real time before flue gas enters a catalyst, regulating ammonia injection branch pipe remote electric control regulating valves corresponding to each section to control ammonia supply amount of each section in real time according to a preset molar ratio of ammonia and nitrogen, and keeping the actually measured molar ratio of ammonia and nitrogen to be identical to the preset molar ratio of ammonia and nitrogen so as to prevent excessive ammonia injection and ensure even concentration distribution of nitric oxides at a denitration system outlet.

Description

A kind of coal-burning boiler SCR denitration control method and control system
Technical field
Pollutant in Coal Burning Boiler emission treatment field of the present invention, particularly a kind of coal-burning boiler SCR denitration control system.
Background technology
Increasingly strict with thermal power plant's pollutant emission standard, selective-catalytic-reduction denitrified (SCR) turns into coal-fired pot The essential part of stove, with liquefied ammonia or urea as reducing agent, reduction NOx turns into N to SCR2And H2O, unreacted in course of reaction Complete NH3Discharged with flue gas in the form of escape ammonia, while a small amount of SO can be produced during coal-fired boiler combustion3, unreacted NH3And SO3And the water in flue gas occurs combination reaction and generates ammonium hydrogen sulfate (ABS), chemical equation is:By equation understand ammonium hydrogen sulfate reaction rate mainly with flue-gas temperature, flue gas in Escape NH3Concentration, SO3Concentration and H2O concentration is relevant.
Ammonium hydrogen sulfate is presented gaseous state, liquid, graininess respectively at different temperature.Gaseous state or graininess ammonium hydrogen sulfate meeting As flue gas flows through air preheater, influence will not be produced on air preheater.And liquid sulfuric acid hydrogen ammonium catches flying dust ability pole By force, can be combined with the fly ash particle in flue gas, be attached to the dust stratification for being formed on air preheater heat transfer element and melting salt shape, caused Stifled ash of the burn into of preheater etc., and then influence the heat exchange of preheater and the normal operation of unit.Therefore, ammonia nitrogen is reasonably controlled Mol ratio and ammonia spraying amount, can control ammonia slip concentration from source, the generation of ammonium hydrogen sulfate is reduced or avoided.
Current SCR denitrating flue gas automatic control modes are broadly divided into three classes.
(1) according to the NH for determining3/ NOx mol ratios are come the gas ammonia flow (efficiency tracking) required for providing.
(2) required gas ammonia flow (concentration tracing) is provided according to the denitrating system exit NOx concentration of setting.
(3) control model based on Neural Network Self-learning.
First two control mode is referred to as traditional control mode, and measurement signal has a hysteresis quality of long period, flue gas with NH3There is strong nonlinearity in the time complexity under catalyst action, it is difficult to be accurately controlled ammonia spraying amount.Based on neutral net certainly The control model of study, the integrated learning main state variables information relevant with denitration efficiency, the network model training objective is cigarette Gas exports deviation minimum between NOx content and setting value, asks for optimal ammonia spraying amount, and the model has adaptivity, self study work( Can, can be good at solving the deficiency that traditional PID control is brought.
But above-mentioned control mode existing defects include:
1, control extensive:Current SCR system smoke components on-line monitoring system is generally sampled using extraction-type single-point, i.e., To multi-channel flue-gas entrance and multi-way outlet, a monitoring point is only set, the representativeness of Monitoring Data is not strong with real-time, ignores The inhomogeneities of NOx regionals distribution, therefore be easy to produce extensive control in actual control.
2, carry out theoretical calculation according to efficiency tracking or concentration tracing and then control the aperture of the spray total pitch of ammonia, theory meter Calculating cannot match with the NOx concentration distribution in SCR flow fields all the time, so as to cause NOx removal rate to decline and NH3The phenomenon of escape Occur.
The content of the invention
It is an object of the invention to provide a kind of coal-burning boiler SCR denitration control method and control system, it is used to solve existing Control method ammonia spraying amount is not enough or excess problem;Further, additionally it is possible to overcome NOx skewness single-point to sample what is caused Extensive control problem.
To achieve the above object, the solution of the present invention includes:
A kind of coal-burning boiler SCR denitration control method, detection is counted into NOx concentration and ammonia density in flue gas before catalyst Calculation obtains ammonia nitrogen mol ratio before catalyst;According to default exhanst gas outlet NOxNOx concentration in flue gas before concentration and entrance catalyst Difference size, calculate preset ammonia nitrogen mol ratio;With preset ammonia nitrogen mol ratio as desired value, the ammonia nitrogen mol ratio before catalyst is Feedforward amount, ammonia spraying amount is controlled by automatic control algorithm.
SCR device is divided into some subregions on the vertical cross-section that flue gas advances, the corresponding smoke inlet chamber of each subregion Room is equipped with before corresponding ammonia-gas spraying device, catalyst ammonia density detection means before NOx concentration detection means and catalyst;Each point Area is independently acquired and controls.
The ammonia nitrogen mol ratio of each subregion isniIt is i-th ammonia nitrogen mole of subregion Than,It is NO2Molal quantity,It is NH3Molal quantity,It is ammonia density before catalyst,Before catalyst NOx concentration;
Each preset ammonia nitrogen mol ratio of subregionIt is NO before SCR catalystxConcentration,It is NO in default exiting flue gasxConcentration.
The automatic control algorithm includes pid algorithm or neural network algorithm.
Coal-burning boiler SCR denitration control system, including the smoke inlet chamber that is sequentially communicated, catalyst chamber, flue gas go out Oral chamber, coal-burning boiler SCR denitration system is divided into some subregions on the vertical cross-section that flue gas advances, the corresponding cigarette of each subregion Gas inlet chamber is equipped with ammonia density detection before NOx concentration detection means (2) and catalyst before corresponding ammonia-gas spraying device, catalyst Device (3);Also include controller (1), NOx concentration detection means (2) before the catalyst of controller sampling connection each subregion With ammonia density detection means (3) before catalyst, the ammonia-gas spraying device of control connection each subregion.
Ammonia-gas spraying device includes several nozzles, nozzle connection spray ammonia house steward (5), the spray ammonia branch between spray ammonia house steward and nozzle Road is provided with regulating valve (4).
The corresponding exhanst gas outlet chamber of each subregion is provided with detection means after the catalyst of NOx concentration in detection gas.
NOx concentration and ammonia density before preset NOx concentration, catalyst are introduced in control of the invention, being capable of maximum journey The guarantee of degree is not in that spray ammonia is excessive or spray ammonia is not enough, and ammonia consumption is reduced while then making guarantee denitration efficiency. The real-time monitoring of ammonia nitrogen mol ratio before catalyst, controllable in real time is realized, can effectively control SCR denitration system to export the escaping of ammonia dense Degree, it is to avoid the equipment fault such as air preheater, deduster and wet denitration system jams, corrosion that ammonia slip concentration is excessively caused, Drastically increase the security and stability of unit operation.
Further, by whole system subregion, partition zone optimizing control is realized in each subregion independent sample, control, can be made Each subregion exit NOx concentration value of SCR denitration system is consistent, and reduces exit NOx concentration spread standard deviation, extends catalyst Service life.
Brief description of the drawings
Fig. 1 is the denitrating system of the embodiment of the present invention 2.
Specific embodiment
The present invention will be further described in detail below in conjunction with the accompanying drawings.
Embodiment 1
Of the invention different from existing control method as a kind of control method, ammonia nitrogen mol ratio is preceding before choosing catalyst Feedback amount, preset ammonia nitrogen mol ratio is target, and the regulating valve of ammonia-gas spraying device is controlled by automatic control algorithms such as such as PID controls, with Control ammonia spraying amount.
Specifically, before catalyst ammonia nitrogen mol ratio be catalyst before the ratio between NOx concentration and ammonia density be worth it with corresponding mole The product of ratio;And preset ammonia nitrogen mol ratio is converted into the difference of NOx concentration and preset NOx concentration before catalyst, before catalyst The ratio between NOx concentration.
NOx concentration and ammonia density before preset NOx concentration, catalyst are introduced in control, can farthest be ensured Be not in that spray ammonia is excessive or spray ammonia is not enough, ammonia consumption is reduced while then making guarantee denitration efficiency.
Embodiment 2
As shown in Figure 1 for a kind of coal-burning boiler SCR denitration system of the embodiment of the present invention, including the flue gas being sequentially communicated enter Oral chamber, catalyst chamber, exhanst gas outlet chamber, coal-burning boiler SCR denitration system are divided on the vertical cross-section that flue gas advances Some regions, the corresponding smoke inlet chamber in each region is equipped with NOx concentration detection dress before corresponding ammonia-gas spraying device, catalyst Ammonia density detection means 3 before 2 and catalyst is put, ammonia density detection means 3 is in ammonia-gas spraying device downstream before catalyst.
Ammonia-gas spraying device includes several nozzles, nozzle connection spray ammonia house steward 5, the spray ammonia branch road between spray ammonia house steward and nozzle It is provided with regulating valve 4.Detection means output signal is connected to controller 1 before catalyst.
After coal-burning boiler denitrating system ammonia-spraying grid 10, flue gas enter catalyst before, install NH3Detected with NOx concentration and filled Put, for real-time monitoring concentration.Each real-time ammonia nitrogen mol ratio of subregionIn each spray ammonia branch pipe peace Remote electrically controlled regulating valve, ammonia flow on-Line Monitor Device are filled, being capable of each subregion NH of real-time monitoring3For amount;Entered according to each subregion Mouth NOx actual measured values and correspondence subregion outlet NOx preset value calculations go out preset ammonia nitrogen mol ratio n 'i
According to DL/T 260《Coal-fired plant flue gas denitrification apparatus performance acceptance test specification》, each subregion Ammonia nitrogen mol ratioAccording to process control needs,Level off to zero, thereforeiThe denitration efficiency of each subregion,Ammonia slip concentration,It is SCR NO before catalystxConcentration,It is NO in default exiting flue gasxConcentration).Ammonia nitrogen mol ratio is surveyed as preceding with each subregion Feedback signal, with preset ammonia nitrogen mol ratio as desired value, by PLC or DCS (PID or with the control based on Neural Network Self-learning Pattern) each subregion correspondence spray remote electrically controlled regulating valve of ammonia subregion is automatically controlled, make actual measurement ammonia nitrogen mol ratio with preset ammonia nitrogen mole Than consistent, i.e. n=n 'ii, reach the purpose of ammonia spraying amount optimization.
As other embodiment, it is also an option that other formula calculate ammonia nitrogen mol ratio, such as formula is deformed Or inlet coefficient etc..
In order to detect exhanst gas outlet situation, the NOx concentration in the corresponding exhanst gas outlet chamber of each subregion is provided with detection gas Catalyst after detection means.
Specific embodiment is presented above, but the present invention is not limited to described implementation method.Base of the invention This thinking is above-mentioned basic scheme, and for those of ordinary skill in the art, various changes are designed in teaching of the invention The model of shape, formula, parameter simultaneously need not spend creative work.It is right without departing from the principles and spirit of the present invention Change, modification, replacement and the modification that implementation method is carried out are still fallen within protection scope of the present invention.

Claims (4)

1. a kind of coal-burning boiler SCR denitration control method, it is characterised in that
Detection is calculated ammonia nitrogen mol ratio before catalyst into NOx concentration and ammonia density in flue gas before catalyst;
According to default exhanst gas outlet NOxConcentration and the difference size into NOx concentration in flue gas before catalyst, calculate preset ammonia Nitrogen mol ratio;
With preset ammonia nitrogen mol ratio as desired value, the ammonia nitrogen mol ratio before catalyst is feedforward amount, by automatic control algorithm control Ammonia spraying amount processed.
2. a kind of coal-burning boiler SCR denitration control method according to claim 1, it is characterised in that by SCR device in cigarette It is divided into some subregions on the vertical cross-section that gas advances, the corresponding smoke inlet chamber of each subregion is equipped with corresponding spray ammonia dress Put, ammonia density detection means before NOx concentration detection means and catalyst before catalyst;Each subregion is independently acquired and controls System.
3. a kind of coal-burning boiler SCR denitration control method according to claim 2, it is characterised in that each subregion Ammonia nitrogen mol ratio isniIt is i-th ammonia nitrogen mol ratio of subregion,It is NO2Molal quantity,It is NH3Molal quantity,It is ammonia density before catalyst,It is NOx concentration before catalyst;
Each preset ammonia nitrogen mol ratio of subregion It is NO before SCR catalystxConcentration,It is NO in default exiting flue gasxConcentration.
4. a kind of coal-burning boiler SCR denitration control method according to claim 1, it is characterised in that described to automatically control Algorithm includes pid algorithm or neural network algorithm.
CN201410527517.6A 2014-10-09 2014-10-09 Coal-fired boiler SCR (Selective Catalytic Reduction) denitration control method and system Active CN104226110B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410527517.6A CN104226110B (en) 2014-10-09 2014-10-09 Coal-fired boiler SCR (Selective Catalytic Reduction) denitration control method and system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410527517.6A CN104226110B (en) 2014-10-09 2014-10-09 Coal-fired boiler SCR (Selective Catalytic Reduction) denitration control method and system

Publications (2)

Publication Number Publication Date
CN104226110A CN104226110A (en) 2014-12-24
CN104226110B true CN104226110B (en) 2017-05-24

Family

ID=52215540

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410527517.6A Active CN104226110B (en) 2014-10-09 2014-10-09 Coal-fired boiler SCR (Selective Catalytic Reduction) denitration control method and system

Country Status (1)

Country Link
CN (1) CN104226110B (en)

Families Citing this family (27)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104678761B (en) * 2015-02-11 2017-04-26 国家电网公司 Total air volume advanced control-based denitration control method and system for thermal power unit
CN104826492B (en) * 2015-04-23 2017-02-22 华北电力大学(保定) Improvement method for selective catalytic reduction flue gas denitrification and ammonia injection control system
CN104841271A (en) * 2015-05-27 2015-08-19 山东应天节能环保科技有限公司 Desulfurization and denitrification automatic control system
CN105045089A (en) * 2015-06-19 2015-11-11 大唐华银电力股份有限公司金竹山火力发电分公司 Boiler denitration control method based on outlet NOx content control and system thereof
CN104965021B (en) * 2015-07-24 2018-05-04 中国科学院重庆绿色智能技术研究院 A kind of coal-fired flue gas denitration catalyst performance evaluation device and method
CN105446137A (en) * 2015-12-15 2016-03-30 国网山东省电力公司电力科学研究院 Thermal power generating unit ammonia spraying automatic control method and thermal power generating unit ammonia spraying automatic control system capable of eliminating large hysteresis quality
CN105597538B (en) * 2015-12-22 2017-12-22 河北省电力建设调整试验所 A kind of denitrification reducing agent based on time difference matching adds control method and its control device
CN107088363B (en) * 2016-02-24 2020-10-09 国网河北能源技术服务有限公司 Denitration unit distribution control and adjustment method based on multidimensional parameters
CN105786035B (en) * 2016-03-29 2018-07-20 东南大学 Fired power generating unit SCR denitration Optimal Control System based on heuristic Prediction and Control Technology
CN105854598A (en) * 2016-05-11 2016-08-17 中国大唐集团科学技术研究院有限公司华东分公司 Uniform ammonia spraying system and method for controlling same
CN106000087A (en) * 2016-05-12 2016-10-12 西安西热锅炉环保工程有限公司 High-performance SCR ultra-low emission control system based on subarea mixed adjustment
CN106215671B (en) * 2016-09-09 2018-10-16 中国大唐集团科学技术研究院有限公司华中分公司 A kind of thermal power plant's denitration spray ammonia control method and device
CN106621804B (en) * 2016-11-15 2020-05-22 国家电网公司 Flue gas ammonia injection mixing device and SCR flue gas denitration system
CN106334444A (en) * 2016-11-17 2017-01-18 西南化工研究设计院有限公司 Low temperature continuous denitrification process for coke oven smoke and reactor thereof
CN106390717B (en) * 2016-11-30 2023-05-23 东方电气集团东方锅炉股份有限公司 Denitration flue for combined denitration of SCR and SNCR
CN106647610A (en) * 2017-02-04 2017-05-10 华北电力大学(保定) Intelligent SCR (Selective Catalytic Reduction) denitration control system and control method thereof
CN107252630B (en) * 2017-05-31 2019-10-29 国家电网公司 A method of optimization SCR denitration system ammonia nitrogen molar ratio distribution
CN107349786A (en) * 2017-07-06 2017-11-17 大唐东北电力试验研究所有限公司 Selective catalytic reduction denitration device and its spray ammonia optimization method
CN108380043B (en) * 2018-02-12 2020-08-14 南京博沃科技发展有限公司 Selective ammonia injection regulation control method for SCR (Selective catalytic reduction) denitration device
CN109236427B (en) * 2018-09-14 2020-11-03 国家能源投资集团有限责任公司 Ammonia spraying control method and device for SCR system, storage medium and processor
CN109055733B (en) * 2018-10-29 2020-02-14 中冶长天国际工程有限责任公司 Method, device and system for removing NOx from grate-rotary kiln
CN109821417A (en) * 2019-03-29 2019-05-31 大唐贵州发耳发电有限公司 A kind of denitrating system ammonia-spraying grid optimization system and its optimization method
CN110038426A (en) * 2019-04-13 2019-07-23 程琛 A kind of frequency modulation type is intelligent to control ammonia system and method
CN111632493B (en) * 2020-06-22 2022-03-22 郑州光力景旭电力技术有限公司 Denitration system, control method thereof and ammonia injection control device
CN113818949A (en) * 2021-10-26 2021-12-21 无锡威孚力达催化净化器有限责任公司 Method for testing concentration of NOx in automobile exhaust, mixing device and aftertreatment system
CN114326384B (en) * 2021-11-24 2024-04-09 海南热带海洋学院 Control method of SCR flue gas denitration system of thermal power plant
CN114870627B (en) * 2022-05-30 2023-08-01 西安热工研究院有限公司 SCR denitration partition accurate ammonia injection control method and system for coal-fired power plant

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN201632195U (en) * 2010-04-06 2010-11-17 东南大学 Fume denitration device with ammonia injection grid having regulation capability
CN103728994A (en) * 2013-12-30 2014-04-16 北京工业大学 Cement plant SCR denitration efficiency monitoring control method

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH10109018A (en) * 1996-10-04 1998-04-28 Babcock Hitachi Kk Waste gas denitration method and device therefor

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN201632195U (en) * 2010-04-06 2010-11-17 东南大学 Fume denitration device with ammonia injection grid having regulation capability
CN103728994A (en) * 2013-12-30 2014-04-16 北京工业大学 Cement plant SCR denitration efficiency monitoring control method

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
"燃煤电站SCR烟气脱硝喷氨自动控制方式优化";罗子湛等;《电站系统》;20100731;第59-60,63页 *

Also Published As

Publication number Publication date
CN104226110A (en) 2014-12-24

Similar Documents

Publication Publication Date Title
CN104226110B (en) Coal-fired boiler SCR (Selective Catalytic Reduction) denitration control method and system
CN105404145B (en) The new cascade control method of denitration based on exponential forecasting and time lag predictive compensation
CN105597537B (en) Denitration control method based on Prediction and Control Technology
CN203899439U (en) Novel SNCR (selective non-catalytic reduction) denitration system
CN105920997B (en) A kind of coal-burning boiler denitrating system that burnout degree is coupled with SNCR and method
CN108628177A (en) A kind of SCR denitration intelligence spray ammonia optimization method and system based on model adaptation PID
CN108195993B (en) Full-size performance detection and evaluation device for SCR denitration catalyst and application method thereof
CN205461808U (en) SCR denitration catalyst on -line measuring with spout ammonia and optimize automatic regulating system
CN103728994B (en) A kind of cement plant SCR denitration efficiency monitoring control method
CN215066412U (en) Ammonia decomposition catalyst performance evaluation device of real flue gas
CN108837698A (en) Based on advanced measuring instrumentss and the SCR denitration of advanced control algorithm spray ammonia optimization method and system
CN102654776A (en) Smoke denitration ammonia injection amount control method and device
CN209387613U (en) Portable spray ammonia levels intelligent measure analysis system
CN109445383A (en) A kind of SCR subregion spray ammonia optimal control method of the preposition static mixer of band
CN107670474B (en) SNCR (selective non-catalytic reduction) denitration system control device and denitration control method
CN110263452A (en) Flue gas Annual distribution characteristic analysis method, system and denitrating system in a kind of flue
CN108816043A (en) A kind of denitration device and its autocontrol method
CN106845134B (en) A kind of boiler controller system relative performance index calculation method and device
CN104147912A (en) Flue-gas denitration method and device by mixing of selective non-catalytic reduction method SNCR and selective catalytic reduction method SCR
CN106295166A (en) A kind of SCR denitration device amount of ammonia slip measuring method and application thereof
CN106076115A (en) The flow field detecting system of SCR denitration technique
CN208097812U (en) A kind of equipment for denitrifying flue gas
CN207187485U (en) Wet flue gas desulfurization oxidation fan energy saving system
CN109933884B (en) Neural network inverse control method for SCR denitration system of coal-fired unit
CN204637957U (en) A kind of equipment for denitrifying flue gas

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant