CN107441669A - A kind of method of heterogeneous catalysis hydrolysis melamine, cyanuric acid and melamine OAT waste residues - Google Patents

A kind of method of heterogeneous catalysis hydrolysis melamine, cyanuric acid and melamine OAT waste residues Download PDF

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Publication number
CN107441669A
CN107441669A CN201610373976.2A CN201610373976A CN107441669A CN 107441669 A CN107441669 A CN 107441669A CN 201610373976 A CN201610373976 A CN 201610373976A CN 107441669 A CN107441669 A CN 107441669A
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Prior art keywords
melamine
waste residues
cyanuric acid
oat
oat waste
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CN107441669B (en
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张涛
唐盛伟
梁斌
龚海
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Sichuan University
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Sichuan University
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    • AHUMAN NECESSITIES
    • A62LIFE-SAVING; FIRE-FIGHTING
    • A62DCHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D3/00Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances
    • A62D3/30Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents
    • A62D3/35Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents by hydrolysis
    • AHUMAN NECESSITIES
    • A62LIFE-SAVING; FIRE-FIGHTING
    • A62DCHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D2101/00Harmful chemical substances made harmless, or less harmful, by effecting chemical change
    • A62D2101/20Organic substances
    • A62D2101/26Organic substances containing nitrogen or phosphorus

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  • Health & Medical Sciences (AREA)
  • General Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Business, Economics & Management (AREA)
  • Emergency Management (AREA)
  • Processing Of Solid Wastes (AREA)
  • Catalysts (AREA)

Abstract

The present invention relates to the method for a kind of heterogeneous catalysis hydrolysis melamine, cyanuric acid and melamine OAT waste residues, catalyst is made using activated alumina or boehmite, in closed pressure vessel, carry and hydrolyzed under pressure, temperature is 190 DEG C ~ 240 DEG C, melamine, cyanuric acid and melamine OAT waste residues can be decomposed into ammonia and carbon dioxide, the wherein main component of melamine OAT waste residues is melamine, ammeline, ammelide, cyanuric acid.At the same time, ammonia caused by hydrolysis and carbon dioxide are the unstripped gas for producing urea, can be with urea plant coproduction, therefore process provides a kind of method of effective resource recycling, suitable for the industrial enterprise of current production melamine.

Description

A kind of heterogeneous catalysis hydrolysis melamine, cyanuric acid and melamine OAT waste residues Method
Technical field
The present invention relates to a kind of heterogeneous catalysis hydrolysis melamine, cyanuric acid and melamine OAT waste residue methods, category In fixed-end forces and recycling economy technical field.
Background technology
Melamine is widely used in synthetic plastic, water soluble paint, viscous glutinous as a kind of important chemical intermediate Agent, fiber and fire retardant.The global demand to melamine in 2015 is all constantly increasing every year at 2,000,000 tons or so It is long.In the technique of Production of Melamine by High Pressure Process, melamine OAT waste residues can be produced, yield is quite huge, and these waste residues are such as Fruit can not obtain relatively reasonable disposal, and environment will certainly be affected, while can also reduce chemical resource Utilization rate.The main component of melamine OAT waste residues is melamine, ammeline, ammelide, trimerization Cyanic acid, they are all the nitrogen-containing compounds containing triazine ring, generally highly stable, it is difficult to by general physically or chemically Method is degraded.It is at present industrially to use high-temperature high-pressure hydrolysis, without using catalyst, directly by three under 285 DEG C, 8.5MPa Poly cyanamid OAT waste residues are decomposed into ammonia and carbon dioxide, and ammonia and carbon dioxide are also the unstripped gas of production urea simultaneously.This method The green circulatory production of melamine is realized, but the higher hydrolysis temperature of this method and pressure make it that operation energy consumption is higher, it is right Equipment requirement is harsh, have impact on the application and popularization of technique.Therefore using the method for catalyzing hydrolysis, reaction temperature is reduced, so as to Reducing the utilization of the running cost and equipment investment of hydrolysis for melamine OAT has important practical value.
It is otherwise using also having carried out to melamine OAT waste residues in addition to foregoing high-temperature high-pressure hydrolysis Research, but all fail to industrialize.A kind of method is that the various components separated in OAT are used, and is such as separated by adjusting pH value Melamine [WO in OAT:0136397 A1], but a large amount of soda acid amounts are consumed in technique, and only reclaimed melamine therein Amine;It can also be separated according to each component sublimation point difference, but higher [the Saito S. Sublimatographic of energy consumption analysis; Sublimatographic separation of melamine, ammerine, ammeride and cyanuric acid[J]. Japan analyst, 1978, 27: 321-325.].Another method is to utilize melamine OAT waste residues prepare other products, such as prepare sulfonated amino resin, or prepare cyanuric acid, but due to OAT complicated components, prepare Obtained product active ingredient is low, complex process [Lahalih SM, Absihalabi M. Recovery of solids from melamine waste effluents and their conversion to useful products[J]. Ind Eng Chem Res. 1989,28(4):500-504;EP:0124710,1984;US:4963674.1990;Ren Baozeng, Luo Ting Bright, the such as Li Chen prepares cyanuric acid environment [J] environmental projects with the solid waste discharged in Melamine Production, and 2003,21 (4):4-44]。
Using activated alumina or boehmite as catalyst in the present invention, can under relatively low temperature conditionss, Melamine, cyanuric acid or melamine OAT waste residues are hydrolyzed to ammonia and carbon dioxide, effectively improve conventional high-temperature high pressure The shortcomings that Hydrolyze method.
The content of the invention
The present invention relates to the method for a kind of heterogeneous catalysis hydrolysis melamine, cyanuric acid and melamine OAT waste residues, Compared with existing industrial treatment OAT waste residue technologies, the beneficial effects of the invention are as follows the reaction for reducing traditional industry hydrolysis process Temperature, so as to reduce energy consumption and the excessive demand to equipment, realize efficient, green solid waste recovery and Utilize.Specific technical scheme is as follows:
It will be placed in autoclave, protect containing melamine, the solution of cyanuric acid or melamine OAT waste residues or suspension Certain liquid-solid ratio is held, at 190 ~ 240 DEG C, makees catalyst using activated alumina or boehmite, system carries pressure Under continuously stir 1 ~ 10h of reaction, you can melamine, cyanuric acid or melamine OAT waste residues are hydrolyzed to ammonia and titanium dioxide Carbon.
Process conditions are that the concentration of melamine, cyanuric acid or melamine OAT waste residues is 0.05g/L ~ 20g/L, The activated alumina of addition or the mass ratio of boehmite catalyst are 0.1% ~ 10%, and reaction temperature is 190 ~ 240 DEG C, Reaction time is 1 ~ 10 h.
The method of heterogeneous catalysis hydrolysis melamine OAT waste residues of the present invention, reaction principle used are:Trimerization Cyanamide, ammeline, ammelide are under the catalytic action of activated alumina or boehmite, its triazine Amino on ring is gradually substituted by hydroxyl, ultimately produces cyanuric acid, and cyanuric acid is further hydrolyzed to ammonia and titanium dioxide Carbon.Its course of reaction such as accompanying drawing 1.
Brief description of the drawings
Fig. 1 is melamine, ammeline, ammelide, cyanuric acid in activated alumina or intends thin water The hydrolysis path profile of ammonia and carbon dioxide is progressively hydrolyzed under the catalytic action of aluminium stone.
Embodiment
For preferably the present invention will be described, it is as follows to enumerate embodiment:
Embodiment 1
Melamine initial concentration is 0.67g/L, and the mass ratio for adding activated alumina is 3.8%, and reaction temperature is 220 DEG C, instead It is 5 hours between seasonable, solution after reaction is detected, the degradation rate of melamine is 99.8%, the yield of ammonia and carbon dioxide For 96.1%.
Embodiment 2
Melamine initial concentration is 2.4g/L, and the mass ratio for adding boehmite is 4.6%, and reaction temperature is 200 DEG C, instead It is 7 hours between seasonable, solution after reaction is detected, the degradation rate of melamine is 93.2%, the yield of ammonia and carbon dioxide For 91.7%.
Embodiment 3
Cyanuric acid initial concentration is 0.67g/L, and the mass ratio for adding activated alumina is 3.8%, and reaction temperature is 220 DEG C, instead It is 2 hours between seasonable, solution after reaction is detected, the degradation rate of cyanuric acid is 98.4%, the yield of ammonia and carbon dioxide For 97.5%.
Embodiment 4
Cyanuric acid initial concentration is 5.0g/L, and the mass ratio for adding boehmite is 1.2%, and reaction temperature is 190 DEG C, instead It is 6 hours between seasonable, solution after reaction is detected, the degradation rate of cyanuric acid is 99.1%, the yield of ammonia and carbon dioxide For 98.4%.
Embodiment 5
Melamine OAT waste residues initial concentration is 16.67g/L, and the mass ratio for adding activated alumina is 3.6%, and reaction temperature is 220 DEG C, the reaction time is 7 hours, and solution after reaction is detected, and the degradation rate of melamine OAT waste residues is 93.4%, ammonia Yield with carbon dioxide is 92.0%.
Embodiment 6
Melamine OAT waste residues initial concentration is 10.0g/L, and the mass ratio for adding boehmite is 2.8%, and reaction temperature is 200 DEG C, the reaction time is 8 hours, and solution after reaction is detected, and the degradation rate of melamine OAT waste residues is 91.7%, ammonia Yield with carbon dioxide is 90.4%.
Embodiment 7
Melamine OAT waste residues initial concentration is 20.0g/L, and the mass ratio for adding activated alumina is 7.9%, and reaction temperature is 240 DEG C, the reaction time is 6 hours, and solution after reaction is detected, and the degradation rate of melamine OAT waste residues is 94.7%, ammonia Yield with carbon dioxide is 92.5%.

Claims (4)

1. a kind of method of heterogeneous catalysis hydrolysis melamine, cyanuric acid and melamine OAT waste residues, it is characterised in that A certain amount of melamine, cyanuric acid and melamine OAT waste residues use active oxidation in the closed pressure resistant container containing water Aluminium or boehmite make catalyst, are heated to temperature as 190 DEG C ~ 240 DEG C, keep system pressure itself, continuous heating stirring 1 ~ 10h, until melamine, cyanuric acid and melamine OAT waste residues are hydrolyzed to ammonia and carbon dioxide.
A kind of 2. method of heterogeneous catalysis hydrolysis melamine OAT waste residues according to claim 1, it is characterised in that Described is heterogeneous for the solid catalyst system and catalyzing of liquid.
A kind of 3. method of heterogeneous catalysis hydrolysis melamine OAT waste residues according to claim 1, it is characterised in that Described catalyst is activated alumina or boehmite.
A kind of 4. method of heterogeneous catalysis hydrolysis melamine OAT waste residues according to claim 1, it is characterised in that The concentration of melamine, cyanuric acid or melamine OAT waste residues is 0.05g/L ~ 20g/L, the activated alumina of addition or The mass ratio of boehmite catalyst is 0.1% ~ 10%, and reaction temperature is 190 ~ 240 DEG C, and the reaction time is 1 ~ 10 h。
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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110216135A (en) * 2019-07-16 2019-09-10 科盛环保科技股份有限公司 A kind of multistage decyanation tower of cyanamide waste residue
CN110772986A (en) * 2019-11-29 2020-02-11 四川金象赛瑞化工股份有限公司 Melamine tail gas purification method, melamine tail gas purification device and application thereof
WO2023104580A1 (en) 2021-12-09 2023-06-15 Basf Se Process for treating triazine-containing wastewater

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20100111062A (en) * 2009-04-06 2010-10-14 티에이치바이오제닉스주식회사 Composition for decomposing melamine
CN201907981U (en) * 2010-12-20 2011-07-27 重庆建峰工业集团有限公司 Cracking system for treatment of melamine wastewater
CN102321037A (en) * 2011-06-02 2012-01-18 郑州大学 Melamine ornithine aminotransferase (OAT) waste residue resource utilization method
CN104370404A (en) * 2014-10-22 2015-02-25 陕西华陆化工环保有限公司 Melamine device wastewater treatment method and treatment system thereof

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20100111062A (en) * 2009-04-06 2010-10-14 티에이치바이오제닉스주식회사 Composition for decomposing melamine
CN201907981U (en) * 2010-12-20 2011-07-27 重庆建峰工业集团有限公司 Cracking system for treatment of melamine wastewater
CN102321037A (en) * 2011-06-02 2012-01-18 郑州大学 Melamine ornithine aminotransferase (OAT) waste residue resource utilization method
CN104370404A (en) * 2014-10-22 2015-02-25 陕西华陆化工环保有限公司 Melamine device wastewater treatment method and treatment system thereof

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110216135A (en) * 2019-07-16 2019-09-10 科盛环保科技股份有限公司 A kind of multistage decyanation tower of cyanamide waste residue
CN110772986A (en) * 2019-11-29 2020-02-11 四川金象赛瑞化工股份有限公司 Melamine tail gas purification method, melamine tail gas purification device and application thereof
WO2023104580A1 (en) 2021-12-09 2023-06-15 Basf Se Process for treating triazine-containing wastewater

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