CN117427478A - Composite fiber denitration agent and preparation method thereof - Google Patents

Composite fiber denitration agent and preparation method thereof Download PDF

Info

Publication number
CN117427478A
CN117427478A CN202310070920.XA CN202310070920A CN117427478A CN 117427478 A CN117427478 A CN 117427478A CN 202310070920 A CN202310070920 A CN 202310070920A CN 117427478 A CN117427478 A CN 117427478A
Authority
CN
China
Prior art keywords
parts
composite fiber
organic
denitration agent
denitration
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
CN202310070920.XA
Other languages
Chinese (zh)
Inventor
乔钢
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.)
Nanjing Stover Environmental Protection Technology Co ltd
Original Assignee
Nanjing Stover 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 Nanjing Stover Environmental Protection Technology Co ltd filed Critical Nanjing Stover Environmental Protection Technology Co ltd
Priority to CN202310070920.XA priority Critical patent/CN117427478A/en
Publication of CN117427478A publication Critical patent/CN117427478A/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
    • B01D53/46Removing components of defined structure
    • B01D53/54Nitrogen compounds
    • B01D53/56Nitrogen oxides
    • 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

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (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 invention discloses a composite fiber denitration agent and a preparation method thereof, wherein the raw materials of the composite fiber denitration agent comprise the following components in parts by weight: 50-70 parts of composite organic calcium, 20-24 parts of organic grease, 23-32 parts of organic amine, 5-9 parts of amino acid, 2-7 parts of organic acid, 1-2 parts of organic salt and 0.08-0.1 part of salt solution. The composite fiber denitration agent is used for denitration of boiler flue gas and the like. The method is suitable for various biomass boilers, gas boilers and coal-fired boilers; the effective temperature is 700-1000 ℃, and the economical applicable temperature is 780-930 ℃; has the characteristics of high efficiency, no coking, low viscosity and wide applicable temperature range.

Description

Composite fiber denitration agent and preparation method thereof
Technical Field
The invention belongs to the technical field of denitration, and particularly relates to a composite fiber denitration agent and a preparation method thereof.
Background
Nitrogen oxides (NOx) are major atmospheric pollutants that can cause acid rain, photochemical pollution, greenhouse effect, and ozone layer destruction. Nitrogen Oxides (NO) x ) Many kinds are common and include nitrous oxide (N 2 O), nitric Oxide (NO), nitrogen dioxide (NO 2 ) Dinitrogen trioxide (N) 2 O 3 ) Dinitrogen tetroxide (N) 2 O 4 ) And dinitrogen pentoxide (N) 2 O 5 ) In addition, nitric oxide dimer (N 2 O 2 ) Nitrosyl azide (N) 4 O), nitrogen trioxide (NO) 3 ) But mainly NO and NO 2 They are common atmospheric pollutants. Naturally emitted NOx mainly comes from the decomposition of organic matter in the soil and the ocean, belonging to the nitrogen cycle process in nature. NOx emitted by man-made activities, mostly from fossil fuel combustion processes, such as those of automobiles, airplanes, internal combustion engines and industrial kilns; also from processes for the production, use or use of nitric acid, e.g. nitrogen fertilizer plants, plantsIntermediate factories, ferrous metal smelters, etc. NOx has great environmental damage, and is one of the main matters for forming acid rain and the important matter for forming photochemical smog in atmosphere and consumed O 3 Is an important factor of (a). Under high temperature combustion conditions, NOx is mainly present in the form of NO, with about 95% of the initial emissions of NOx. However, NO reacts very easily with oxygen in the air in the atmosphere to form NO 2 Therefore, NOx in the atmosphere is commonly represented by NO 2 Is present in the form of (c). NO and NO in air 2 Equilibrium is achieved by interconversion through photochemical reactions. NO at higher temperatures or in the presence of cloud 2 Further reacts with water molecules to form nitric acid (HNO), a second important acid component in acid rain 3 ). In the presence of a catalyst, e.g. in the presence of suitable weather conditions, NO 2 The conversion rate to nitric acid is increased. In particular when NO 2 With SO 2 When the two components exist simultaneously, the two components can catalyze each other, so that the nitric acid can be formed more quickly. Furthermore, NOx can also build up in concentration as the aircraft emits exhaust gases in the stratosphere, gradually accumulating. NOx re-and-advection layer O 3 React to generate NO and O 2 NO and O 3 Further reaction to produce NO 2 And O 2 Thereby breaking O 3 Balance O 3 Concentration decreases, resulting in O 3 Wear of the layer.
Denitration of coal-fired flue gas is one of the important measures for controlling Nitrogen Oxides (NOX). Flue gas denitration is divided into denitration before combustion, denitration in combustion and denitration after combustion. The denitration before combustion is to perform denitration on fuel coal, and no better method exists in the aspect at present; denitration in combustion is to add a low-nitrogen burner and a staged combustion method in boiler equipment to reduce the generation of nitrogen oxides: the most mature method is widely applied to denitration after combustion, and nitrogen oxides in the flue gas are controlled, and common denitration methods include SCR (selective catalytic reduction), SNCR (selective non-catalytic reduction) and low-temperature-section addition of auxiliary agents.
The flue gas denitration agent mainly comprises urea, ammonia water and an oxidant. Common denitration techniques are SCR and SCNR. SNCR or SCR uses ammonia or urea as a denitration aid, but has a low denitration rate, typically about 50%. Therefore, development of a composite fiber denitration agent with high efficiency, no coking, low viscosity and wide application temperature range is needed.
Disclosure of Invention
The invention aims to provide a composite fiber denitration agent with high efficiency, no coking, low viscosity and wide applicable temperature range and a preparation method thereof.
In order to achieve the above purpose, the invention adopts the following technical scheme:
the composite fiber denitration agent comprises the following raw materials in parts by weight:
50-70 parts of composite organic calcium, 20-24 parts of organic grease, 23-32 parts of organic amine, 5-9 parts of amino acid, 2-7 parts of organic acid, 1-2 parts of organic salt and 0.08-0.1 part of salt solution.
The organic lipid is one of water-soluble lipid and cellulose.
The organic amine is one of acrylamide, carbonamide and polyacrylamide.
The amino acid is one of glycine, arginine and cysteine.
The organic acid is one of acetic acid, acrylic acid, crataegolic acid and oxalic acid.
The organic salt is one of calcium acrylate, sodium glycinate, sodium glutamate and sodium crataegolate.
The solvent is an inorganic salt water solution.
The salt solution is aqueous solution of sodium bicarbonate, calcium bicarbonate, magnesium bicarbonate or calcium sulfate.
The preparation method of the composite fiber denitration agent comprises the following steps: firstly, weighing the raw material components according to the proportion, then fully mixing the raw materials, and uniformly mixing to obtain the water-like composite fiber denitration agent.
The beneficial effects are that: the composite fiber denitration agent is used for denitration of boiler flue gas and the like. The method is suitable for various biomass boilers, gas boilers and coal-fired boilers; the effective temperature is 700-1000 ℃, and the economical applicable temperature is 780-930 ℃; has the characteristics of high efficiency, no coking, low viscosity and wide applicable temperature range. Can be suitable for gas, coal and biomass boilers with lower flue gas temperature, cement kilns, glass kilns and stonesAsh kilns, ceramic kiln paths, and the like. The invention is ammonia-free denitration, has lower denitration temperature and has a removal part S0 2 The denitration depth is highly controllable. Can meet stricter flue gas emission requirements, and has high denitration efficiency which can reach 70-90%.
Detailed Description
The invention will be further explained with reference to examples.
Example 1
The composite fiber denitration agent comprises the following raw materials in parts by weight:
60 parts of composite organic calcium, 24 parts of organic grease, 30 parts of organic amine, 9 parts of amino acid, 5 parts of organic acid, 1 part of organic salt and 0.1 part of solvent.
The organic lipid is water-soluble lipid, the organic amine is acrylamide, the amino acid is glycine, the organic acid is acetic acid, the organic salt is calcium acrylate, and the solvent is sodium bicarbonate water solution.
Firstly, weighing the raw material components according to the proportion, then fully mixing the raw materials, and uniformly mixing to obtain the water-like composite fiber denitration agent.
Example 2
70 parts of composite organic calcium, 20 parts of organic grease, 32 parts of organic amine, 5 parts of amino acid, 2 parts of organic salt and 0.09 part of solvent.
The organic lipid is cellulose, the organic amine is carbonic acid amide, the amino acid is arginine, the organic acid is crataegolic acid, the organic salt is sodium glycinate, and the solvent is aqueous solution of calcium bicarbonate.
Firstly, weighing the raw material components according to the proportion, then fully mixing the raw materials, and uniformly mixing to obtain the water-like composite fiber denitration agent.
Example 3
50 parts of composite organic calcium, 22 parts of organic grease, 23 parts of organic amine, 7 parts of amino acid, 7 parts of organic acid, 2 parts of organic salt and 0.08 part of solvent.
The organic lipid is cellulose, the organic amine is polyacrylamide, the amino acid is cysteine, the organic acid is oxalic acid, the organic salt is sodium crataegolate, and the solvent is aqueous solution of magnesium bicarbonate.
Firstly, weighing the raw material components according to the proportion, then fully mixing the raw materials, and uniformly mixing to obtain the water-like composite fiber denitration agent.
The physical and chemical properties of the composite fiber denitration agent of examples 1 to 3 are as follows:
appearance and properties of dark brown liquid.
The pH value is 9.0-12.0
Freezing point (deg.c): -10 to-15 DEG C
Relative density (water=1000): 1050 to 1090
Boiling point (DEG C) 140 DEG C
Concentration (mass ratio) of 0.6
Viscosity (20deg.C, cp) 2-6 (Water 1.02, diesel oil 30)
Solubility, namely, water and alcohol.
The application method of the composite fiber denitration agent is similar to that of the existing SNCR technology, firstly, a temperature interval (780-930 ℃) which is most suitable for the reaction of the composite fiber denitration agent is selected on a boiler flue, and a plurality of special efficient atomizing nozzles are arranged, so that the denitration agent is fully mixed with flue gas, and the zero-clearance coverage of the denitration reaction in the flue is realized. The prepared composite fiber denitration agent is delivered to a metering and distributing module through a storage tank by a delivery pump, then is accurately distributed to each spraying device, and is sprayed into the tail part of a boiler flue, catalytic cracking reaction is carried out at the high temperature of about 780-930 ℃, and active free radicals generated by cracking and NO in the flue gas are generated x Oxidation-reduction reaction is carried out under the condition of NO catalyst participation, and NO is removed x
Selecting a proper denitration position: the temperature in the non-flame zone is 780-930 ℃. The gas-liquid phase pressure at the spray gun is more than 0.4 MPa. The efficient atomizing spray gun is selected, the flow field simulates atomizing distribution, the zero-clearance coverage rate of the denitration agent liquid mist on the section of the flue is improved as much as possible, and necessary spray gun protection measures are adopted according to the actual condition of the boiler.
The foregoing is merely a preferred embodiment of the present invention and it should be noted that modifications and adaptations to those skilled in the art may be made without departing from the principles of the present invention, which are intended to be comprehended within the scope of the present invention.

Claims (9)

1. A composite fiber denitration agent is characterized in that: the raw materials of the composite material comprise the following components in parts by weight:
50-70 parts of composite organic calcium, 20-24 parts of organic grease, 23-32 parts of organic amine, 5-9 parts of amino acid, 2-7 parts of organic acid, 1-2 parts of organic salt and 0.08-0.1 part of solvent.
2. The composite fiber denitration agent according to claim 1, characterized in that: the organic lipid is one of water-soluble lipid and cellulose.
3. The composite fiber denitration agent according to claim 1, characterized in that: the organic amine is one of acrylamide, carbonamide and polyacrylamide.
4. The composite fiber denitration agent according to claim 1, characterized in that: the amino acid is one of glycine, arginine and cysteine.
5. The composite fiber denitration agent according to claim 1, characterized in that: the organic acid is one of acetic acid, acrylic acid, crataegolic acid and oxalic acid.
6. The composite fiber denitration agent according to claim 1, characterized in that: the organic salt is one of calcium acrylate, sodium glycinate, sodium glutamate and sodium crataegolate.
7. The composite fiber denitration agent according to claim 1, characterized in that: the solvent is an inorganic salt water solution.
8. The composite fiber denitration agent according to claim 7, characterized in that: the salt solution is aqueous solution of sodium bicarbonate, calcium bicarbonate, magnesium bicarbonate or calcium sulfate.
9. A method for preparing the composite fiber denitration agent as claimed in claim 1, which is characterized by comprising the following steps: the method comprises the following steps: firstly, weighing the raw material components according to the proportion, then fully mixing the raw materials, and uniformly mixing to obtain the water-like composite fiber denitration agent.
CN202310070920.XA 2023-02-07 2023-02-07 Composite fiber denitration agent and preparation method thereof Pending CN117427478A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202310070920.XA CN117427478A (en) 2023-02-07 2023-02-07 Composite fiber denitration agent and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202310070920.XA CN117427478A (en) 2023-02-07 2023-02-07 Composite fiber denitration agent and preparation method thereof

Publications (1)

Publication Number Publication Date
CN117427478A true CN117427478A (en) 2024-01-23

Family

ID=89548624

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202310070920.XA Pending CN117427478A (en) 2023-02-07 2023-02-07 Composite fiber denitration agent and preparation method thereof

Country Status (1)

Country Link
CN (1) CN117427478A (en)

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101078517A (en) * 2007-06-08 2007-11-28 华北电力大学 Method for simultaneously removing SO2, NOx from coal-fired furnace
CN104174277A (en) * 2014-08-22 2014-12-03 华中科技大学 Preparation method of efficient desulfurization and denitration agent for coal-fired boiler and application of efficient desulfurization and denitration agent for coal-fired boiler
CN107243244A (en) * 2017-06-16 2017-10-13 中国石油大学(华东) Carbide slag and biological pyrolysis oil prepare biological desulphurization denitrfying agent and its application method
CN111167277A (en) * 2020-01-19 2020-05-19 山东省昔利环境科技有限公司 Preparation method of composite organic calcium-based denitration agent
CN112354336A (en) * 2020-09-15 2021-02-12 山东莱顿能源技术有限公司 Method for preparing desulfurizer and denitrifier from unburned carbon and application
CN113117475A (en) * 2021-04-30 2021-07-16 山东省昔利环境科技有限公司 Composite fiber denitration agent and preparation method thereof

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101078517A (en) * 2007-06-08 2007-11-28 华北电力大学 Method for simultaneously removing SO2, NOx from coal-fired furnace
CN104174277A (en) * 2014-08-22 2014-12-03 华中科技大学 Preparation method of efficient desulfurization and denitration agent for coal-fired boiler and application of efficient desulfurization and denitration agent for coal-fired boiler
CN107243244A (en) * 2017-06-16 2017-10-13 中国石油大学(华东) Carbide slag and biological pyrolysis oil prepare biological desulphurization denitrfying agent and its application method
CN111167277A (en) * 2020-01-19 2020-05-19 山东省昔利环境科技有限公司 Preparation method of composite organic calcium-based denitration agent
CN112354336A (en) * 2020-09-15 2021-02-12 山东莱顿能源技术有限公司 Method for preparing desulfurizer and denitrifier from unburned carbon and application
CN113117475A (en) * 2021-04-30 2021-07-16 山东省昔利环境科技有限公司 Composite fiber denitration agent and preparation method thereof

Similar Documents

Publication Publication Date Title
CA1304914C (en) Reduction of nitrogen- and carbon-based pollutants through the use of urea solutions
CN105289233A (en) Coal-fired boiler SNCR and SCR combined denitration system and method thereof
CN105457465B (en) A kind of SNCR SCR combine the design method of flue gas denitrification system technique
CN202683062U (en) Amino selective non-catalytic reduction (SNCR) flue gas denitration device
CN107149867A (en) Combustion product gases environment-friendly low-temperature composite denitration agent and preparation method thereof
Latha et al. A review on scr system for nox reduction in diesel engine
CN102961956B (en) CFD-based industrial boiler selective non-catalytic reduction (SNCR) denitration device
CN103272470B (en) A kind of additive for improving SNCR ammonia activity and application thereof
CN103252159B (en) Additive for denitration of smoke SNCR (selective non-catalytic reduction) and application thereof
CN109569240A (en) NO_x Reduction by Effective ionic liquid and its application method
CN204933244U (en) NOx removal device in coal-burning power plant's coal-powder boiler flue gas
JPH0857261A (en) Denitrification apparatus using aqueous solution of reducing agent
CN117427478A (en) Composite fiber denitration agent and preparation method thereof
CN104785092A (en) An SNCR flue gas denitration device
CN207356908U (en) A kind of highly-efficient glass kiln exhaust gas denitration device
CN102728215A (en) Composition and method for removing nitrogen oxides in desulfurizing tower
CN102671532B (en) Enhanced selective non-catalytic reduction flue gas denitrification method
CN205145943U (en) Coal fired boiler SNCR and SCR unite deNOx systems
KR20090084055A (en) The reduction agent injection system for increasing nh3 evolution in sncr process
CN105536487A (en) Multi-point injected ammonia water atomization reduction method for reducing NOx discharge of gas-fired boiler
CN220648289U (en) Small-section SNCR spray gun arrangement structure of sludge incinerator
CN102698600A (en) System for intelligently controlling flue gas denitrification of cement plant based on selective catalytic reduction (SCR) method
CN109534359B (en) Ammonia gas preparation device for flue gas denitration system
CN111715050B (en) Method for improving urea denitration efficiency by adopting alkaline alcohol solution
CN113019109A (en) Selective non-catalytic reduction desulfurization method

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