CN106807201A - A kind of denitration method for flue gas of coproduction cyanuric acid - Google Patents

A kind of denitration method for flue gas of coproduction cyanuric acid Download PDF

Info

Publication number
CN106807201A
CN106807201A CN201710066660.3A CN201710066660A CN106807201A CN 106807201 A CN106807201 A CN 106807201A CN 201710066660 A CN201710066660 A CN 201710066660A CN 106807201 A CN106807201 A CN 106807201A
Authority
CN
China
Prior art keywords
denitration
reaction
flue gas
urea
cyanuric acid
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.)
Pending
Application number
CN201710066660.3A
Other languages
Chinese (zh)
Inventor
李蔚
李守顺
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.)
Ji'nan Lihong Environmental Protection Technology Co Ltd
Original Assignee
Ji'nan Lihong Environmental Protection 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 Ji'nan Lihong Environmental Protection Technology Co Ltd filed Critical Ji'nan Lihong Environmental Protection Technology Co Ltd
Priority to CN201710066660.3A priority Critical patent/CN106807201A/en
Publication of CN106807201A publication Critical patent/CN106807201A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/77Liquid phase processes
    • B01D53/78Liquid phase processes with gas-liquid contact
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/54Nitrogen compounds
    • B01D53/56Nitrogen oxides
    • CCHEMISTRY; METALLURGY
    • C07ORGANIC CHEMISTRY
    • C07DHETEROCYCLIC COMPOUNDS
    • C07D251/00Heterocyclic compounds containing 1,3,5-triazine rings
    • C07D251/02Heterocyclic compounds containing 1,3,5-triazine rings not condensed with other rings
    • C07D251/12Heterocyclic compounds containing 1,3,5-triazine rings not condensed with other rings having three double bonds between ring members or between ring members and non-ring members
    • C07D251/26Heterocyclic compounds containing 1,3,5-triazine rings not condensed with other rings having three double bonds between ring members or between ring members and non-ring members with only hetero atoms directly attached to ring carbon atoms
    • C07D251/30Only oxygen atoms
    • C07D251/32Cyanuric acid; Isocyanuric acid

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Treating Waste Gases (AREA)

Abstract

The present invention relates to a kind of denitration method for flue gas of coproduction cyanuric acid, belong to gas cleaning processing technology field.Denitration method for flue gas of the invention, comprises the following steps:Urea condensation reacts, and the ammonia of generation is passed through formalin, is reacted, and the material that the reaction is obtained carries out denitration as denitrfying agent injection denitration reaction area under 500 1100 DEG C of temperature conditionss.The present invention obtains cyanuric acid and liquid denitrfying agent with urea and formaldehyde as raw material by two-step reaction;Then denitration is carried out using liquid denitrfying agent.Urea and formaldehyde are conventional industrial chemicals, cheap, and transport is in the absence of danger, and cost of transportation is low.Cyanuric acid is obtained while denitrfying agent is prepared, cyanuric acid is widely used industrial chemicals.The present invention obtains the two-step reaction of liquid denitrfying agent, is simple reaction, can be completed using microwave reactor and circulating pump.

Description

A kind of denitration method for flue gas of coproduction cyanuric acid
Technical field
The present invention relates to a kind of denitration method for flue gas of coproduction cyanuric acid, belong to gas cleaning processing technology field.
Technical background
With China's expanding economy, the environmental pollution that mass energy consumption brings is increasingly serious.China is used as with coal It is the country of main energy sources, the harmful substance such as contained sulfur dioxide, nitrogen oxides severe contamination air in coal-fired flue-gas, aggravation Haze weather.Nitrogen oxide emission in strict control flue gas is extremely urgent, finds more economical feasible denitrating flue gas skill Art also more shows important.
Traditional denitration technology is selective catalytic reduction reaction technology(SCR)With SNCR reaction technology (SNCR).Wherein, there is the shortcomings of initial outlay is high, smoke components influence is big, operating cost is high in SCR technology;SNCR technologies are deposited Reducing agent with flue gas mixability is poor, denitration efficiency is low, ammonia escaped quantity greatly, high energy consumption the shortcomings of.
Largely using ammonia, the main source of ammonia has liquefied ammonia, ammoniacal liquor and urea to existing denitration technology.Wherein, liquefied ammonia and dense Ammoniacal liquor of the degree more than 8% is harmful influence, and transporting hasardous are high, and freight charges are high;Energy wave in ammoniacal liquor and aqueous solution of urea gasification Take serious, and denitration efficiency itself is low, ammonia escaped quantity is big;Three is not preferable denitrfying agent.
The content of the invention
For the above-mentioned deficiency of existing denitration technology, the present invention provides a kind of coproduction trimerization with urea and formaldehyde as raw material The denitration method for flue gas of cyanic acid.
Technical scheme
A kind of denitration method for flue gas of coproduction cyanuric acid, comprises the following steps:
(1)Urea carries out condensation reaction under the conditions of 200-260 DEG C;Condensation reaction generates cyanuric acid solid;
(2)The ammonia of condensation reaction generation is passed through formalin, is reacted;
(3)Step(2)The reaction mass for obtaining enters as denitrfying agent injection denitration reaction area under 500-1100 DEG C of temperature conditionss Row denitration;
Urea is 1-1.5 with the mol ratio of formaldehyde in formalin:1.
Above-mentioned denitration method for flue gas, the preferably reaction temperature of urea, 220 DEG C.
Above-mentioned denitration method for flue gas, step(2)The reaction mass for obtaining is liquid, and main component is hexa; The present invention is using the liquid material as denitrfying agent;In order to ensure to need guarantee to be passed through first without formaldehyde, the present invention in the denitrfying agent Ammonia excess in aldehyde solution, makes the ph values of the reaction mass for finally giving between 11-12, therefore hexa liquid Contain ammoniacal liquor in denitrfying agent, ammoniacal liquor can improve denitration rate with the common denitration of hexa.But the ammoniacal liquor category of 8% concentrations above In hazardous chemical, it is stored and is required;The mol ratio of formaldehyde in urea and formalin is defined to 1-1.5 by the present invention: 1.Preferably, urea and the mol ratio of formaldehyde in formalin are 1.08-1.35:1.It is furthermore preferred that in urea and formalin The mol ratio of formaldehyde is 1.35:1.
The present invention obtains cyanuric acid and liquid denitrfying agent with urea and formaldehyde as raw material by two-step reaction;Then Denitration is carried out using liquid denitrfying agent.Urea and formaldehyde are conventional industrial chemicals, cheap, and transport is in the absence of danger Property, cost of transportation is low.Cyanuric acid is obtained while denitrfying agent is prepared, cyanuric acid is widely used industrial chemicals. The present invention obtains the two-step reaction of liquid denitrfying agent, is simple reaction, can be completed using microwave reactor and circulating pump.This The used denitration device of invention, can be transformed in the carrying out in the case that boiler or kiln do not stop production, and normal production fortune is not influenceed OK, easily realize.The present invention prepares the two-step reaction of liquid denitrfying agent, and the product of first step reaction a, part is used for second step Reaction a, part is cyanuric acid;Second step reacts, and whole materials are used as denitrfying agent in reaction system;There is no waste material to produce.This Invention is low with scr methods specific investment and operating cost, higher than denitration efficiency with sncr methods, and extra acquisition cyanuric acid is this valuable The chemical products of value.
Above-mentioned denitration method for flue gas, it is preferred that step(3)" the step(2)The reaction mass for obtaining is noted as denitrfying agent Enter denitration reaction area " injection pressure be 500-1000kpa.
Above-mentioned denitration method for flue gas, it is preferred that step(3)Temperature conditionss be 900-1100 DEG C.
Above-mentioned denitration method for flue gas, it is preferred that step(3)The reaction time of denitration reaction is 1-5s.
Above-mentioned denitration method for flue gas, it is preferred that NOx in denitrfying agent in hexa and denitration reaction area mole Than for(0.1-0.8):1, it is further preferred that hexa is with the mol ratio of NOx(0.2-0.5):1.The NOx is Refer to nitrogen oxides.
Beneficial effects of the present invention
1., with urea and formalin as raw material, urea and formalin relative safety are high, and purchase cost is low, no for the present invention There are transporting hasardous, occupation area of equipment is small;Primary construction cost and later stage operating cost are less than SCR technology;Denitration efficiency Higher than SNCR technologies, at the same overcome SNCR technologies high energy consumption, the shortcomings of ammonia escaped quantity is big.
2. during denitrfying agent is prepared, urea condensation reaction generates ammonia and cyanuric acid, cyanuric acid to the present invention Itself it is a kind of chemical products of high added value, with economic benefit.
3. it is of the present invention to carry out the out of stock method of flue gas using urea and formaldehyde joint technology of preparing, it is adaptable to various Industrial Boiler and Industrial Stoves.
Specific embodiment
With reference to example, the present invention will be further described.
Embodiment 1
850kg urea heats generation ammonia and cyanuric acid under the conditions of 220 DEG C.The ammonia for reacting generation is passed through 1000kg first Aldehyde solution(Mass concentration is 37%;Similarly hereinafter)In obtain the mixing liquid of hexa and ammoniacal liquor.Using the mixing liquid as Denitrfying agent is sprayed into pending flue gas, and penetrating pressure is 500kpa, and it is 0.2 with the mol ratio of NOx to control hexa:1, 950 DEG C of maintenance reaction temperature, reacts 2s, and the product that reaction is obtained is N2, CO, CO2, H2O, before detection analysis instrument detection process The concentration of NOx afterwards, it is 82% to calculate NOx removal efficiency.
Embodiment 2
1000kg urea heats generation ammonia and cyanuric acid under the conditions of 220 DEG C.The ammonia for reacting generation is passed through 1000kg The mixing liquid of hexa and ammoniacal liquor is obtained in formalin.Pending cigarette is sprayed into using the mixing liquid as denitrfying agent In gas, penetrating pressure is 500kpa, and it is 0.2 with the mol ratio of NOx to control hexa:1,950 DEG C of maintenance reaction temperature, Reaction 2s, the product that obtains of reaction is N2, CO, CO2, H2O, with the concentration of NOx before and after detection analysis instrument detection process, is calculated It is 84% to go out NOx removal efficiency.
Embodiment 3
1100kg urea exists220Generation ammonia and cyanuric acid are heated under the conditions of DEG C.The ammonia for reacting generation is passed through 1000kg The mixing liquid of hexa and ammoniacal liquor is obtained in formalin.Pending cigarette is sprayed into using the mixing liquid as denitrfying agent In gas, penetrating pressure is 500kpa, and it is 0.2 with the mol ratio of NOx to control hexa:1,950 DEG C of maintenance reaction temperature, Reaction 2s, the product that obtains of reaction is N2, CO, CO2, H2O, with the concentration of NOx before and after detection analysis instrument detection process, is calculated Going out NOx removal efficiency is86%。
Embodiment 4
800Kg urea is 22Generation ammonia and cyanuric acid are heated under the conditions of 0 DEG C.The ammonia for reacting generation is passed through 1000kg first The mixing liquid of hexa and ammoniacal liquor is obtained in aldehyde solution.Pending flue gas is sprayed into using the mixing liquid as denitrfying agent In, penetrating pressure is 500kpa, and it is 0.2 with the mol ratio of NOx to control hexa:1,950 DEG C of maintenance reaction temperature, instead Answer 2s, the product that reaction is obtained is N2, CO, CO2, H2O, with the concentration of NOx before and after detection analysis instrument detection process, calculate NOx removal efficiency is 79%.
Embodiment 5
1000kg urea heats generation ammonia and cyanuric acid under the conditions of 260 DEG C.The ammonia for reacting generation is passed through 1000kg The mixing liquid of hexa and ammoniacal liquor is obtained in formalin.Pending cigarette is sprayed into using the mixing liquid as denitrfying agent In gas, penetrating pressure is 500kpa, and it is 0.2 with the mol ratio of NOx to control hexa:1,950 DEG C of maintenance reaction temperature, Reaction 2s, the product that obtains of reaction is N2, CO, CO2, H2O, with the concentration of NOx before and after detection analysis instrument detection process, is calculated It is 83% to go out NOx removal efficiency.
Embodiment 5
1000kg urea heats generation ammonia and cyanuric acid under the conditions of 200 DEG C.The ammonia for reacting generation is passed through 1000kg The mixing liquid of hexa and ammoniacal liquor is obtained in formalin.Pending cigarette is sprayed into using the mixing liquid as denitrfying agent In gas, penetrating pressure is 500kpa, and it is 0.2 with the mol ratio of NOx to control hexa:1,950 DEG C of maintenance reaction temperature, Reaction 2s, the product that obtains of reaction is N2, CO, CO2, H2O, with the concentration of NOx before and after detection analysis instrument detection process, is calculated It is 82% to go out NOx removal efficiency.

Claims (8)

1. a kind of denitration method for flue gas of coproduction cyanuric acid, it is characterised in that comprise the following steps:
(1)Urea carries out condensation reaction under the conditions of 200-260 DEG C;Condensation reaction generates cyanuric acid solid;
(2)The ammonia of condensation reaction generation is passed through formalin, is reacted;
(3)Step(2)The reaction mass for obtaining enters as denitrfying agent injection denitration reaction area under 500-1100 DEG C of temperature conditionss Row denitration;
Urea is 1-1.5 with the mol ratio of formaldehyde in formalin:1.
2. denitration method for flue gas according to claim 1, it is characterised in that the reaction temperature of urea is 220 DEG C.
3. denitration method for flue gas according to claim 1 or claim 2, it is characterised in that urea with formalin formaldehyde mole Than being 1.08-1.35:1.
4. denitration method for flue gas according to claim 3, it is characterised in that step(3)" the step(2)The reaction for obtaining Material is used as denitrfying agent injection denitration reaction area " injection pressure be 500-1000kpa.
5. denitration method for flue gas according to claim 4, it is characterised in that the temperature conditionss of step 3 are 900-1100 DEG C.
6. denitration method for flue gas according to claim 5, it is characterised in that the reaction time of step 3 denitration reaction is 1-5s.
7. denitration method for flue gas according to claim 6, it is characterised in that hexa and denitration reaction in denitrfying agent The mol ratio of the NOx in area is 0.1-0.8:1.
8. denitration method for flue gas according to claim 7, it is characterised in that in hexa and denitration reaction area The mol ratio of NOx is 0.2-0.5:1.
CN201710066660.3A 2017-02-07 2017-02-07 A kind of denitration method for flue gas of coproduction cyanuric acid Pending CN106807201A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710066660.3A CN106807201A (en) 2017-02-07 2017-02-07 A kind of denitration method for flue gas of coproduction cyanuric acid

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710066660.3A CN106807201A (en) 2017-02-07 2017-02-07 A kind of denitration method for flue gas of coproduction cyanuric acid

Publications (1)

Publication Number Publication Date
CN106807201A true CN106807201A (en) 2017-06-09

Family

ID=59111597

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710066660.3A Pending CN106807201A (en) 2017-02-07 2017-02-07 A kind of denitration method for flue gas of coproduction cyanuric acid

Country Status (1)

Country Link
CN (1) CN106807201A (en)

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102068888A (en) * 2010-12-28 2011-05-25 北京博奇电力科技有限公司 Method for simultaneously desulfurizing and denitrating flue gas by wet method
CN102553412A (en) * 2012-02-10 2012-07-11 山东大学 Method for denitrifying flue gas by using amino reducing agent with high reaction activity
CN103769240A (en) * 2012-10-25 2014-05-07 中国石油化工股份有限公司 Preparation method of catalyst for selective catalytic reduction denitration reactions
CN104014232A (en) * 2014-06-24 2014-09-03 山东大学 Method for performing smoke desulfurization and denitrification by using urea co-production preparation technology
CN104826669A (en) * 2015-04-26 2015-08-12 重庆大学 Alkali washing liquid for regenerating SCR denitration catalysts and application thereof
CN105617818A (en) * 2015-10-12 2016-06-01 江苏蓝电环保股份有限公司 Solvent for recovering SO2 from industrial waste gas

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102068888A (en) * 2010-12-28 2011-05-25 北京博奇电力科技有限公司 Method for simultaneously desulfurizing and denitrating flue gas by wet method
CN102553412A (en) * 2012-02-10 2012-07-11 山东大学 Method for denitrifying flue gas by using amino reducing agent with high reaction activity
CN103769240A (en) * 2012-10-25 2014-05-07 中国石油化工股份有限公司 Preparation method of catalyst for selective catalytic reduction denitration reactions
CN104014232A (en) * 2014-06-24 2014-09-03 山东大学 Method for performing smoke desulfurization and denitrification by using urea co-production preparation technology
CN104826669A (en) * 2015-04-26 2015-08-12 重庆大学 Alkali washing liquid for regenerating SCR denitration catalysts and application thereof
CN105617818A (en) * 2015-10-12 2016-06-01 江苏蓝电环保股份有限公司 Solvent for recovering SO2 from industrial waste gas

Similar Documents

Publication Publication Date Title
CA2063811C (en) Nitrogen oxides reduction using a urea hydrolysate
CN103691271B (en) A kind of flue gas gas phase desulfurization denitration method simultaneously
Yeh et al. Semi-batch absorption and regeneration studies for CO2 capture by aqueous ammonia
CN102553412A (en) Method for denitrifying flue gas by using amino reducing agent with high reaction activity
CN205627636U (en) Be applied to SCR flue gas denitration's reductant preparation mixing arrangement
CN207680368U (en) A kind of equipment for denitrifying flue gas based on temperature-compensating
CN103736377B (en) Method for gas-phase desulfurization of glue gas
CN104014232A (en) Method for performing smoke desulfurization and denitrification by using urea co-production preparation technology
CN107737520A (en) The method that coordinated desulfurization denitration is carried out to Flue Gas of Nonferrous Smelting using sodium alkali is circulated
CN106807201A (en) A kind of denitration method for flue gas of coproduction cyanuric acid
CN106669390B (en) A kind of denitration process method of the process tail gas containing NOx
CN204637957U (en) A kind of equipment for denitrifying flue gas
CN104874270B (en) Method and system for denitration by adopting isocyanic acid gas
CN104607031A (en) Waste gas denitration treatment method and device thereof
CN103301733B (en) Method and device for removing oxynitride in smoke by organic waste
CN102698587A (en) Cement plant flue gas denitration intelligent control system based on SNCR (Selective Non Catalytic Reduction) method
CN109224801A (en) A kind of smoke denitrifier
CN208612149U (en) A set of process system that denitrating flue gas is carried out using urea and formaldehyde coproduction technology of preparing
CN103007751A (en) Process system utilizing preheated air to achieve flue gas denitration
CN208389772U (en) The out of stock system of the iron ammonia process of desulfurization
CN106215681A (en) Flue gas compound desulfurization denitrification agent and preparation method thereof
CN103041676A (en) Method for providing ammonia used for removing sulfur and nitrate from exhaust gas
CN209333525U (en) System for removing nitrite in slurry of calcium-based catalyst for simultaneous desulfurization and denitrification
CN208720184U (en) A kind of waste heat boiler of nitrogen oxides minimum discharge
CN111359396A (en) Coke oven flue gas semi-dry ammonia desulfurization process

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20170609

RJ01 Rejection of invention patent application after publication