CN105771636B - A kind of preparation method of flue gas desulfurization pulvis - Google Patents

A kind of preparation method of flue gas desulfurization pulvis Download PDF

Info

Publication number
CN105771636B
CN105771636B CN201610252905.7A CN201610252905A CN105771636B CN 105771636 B CN105771636 B CN 105771636B CN 201610252905 A CN201610252905 A CN 201610252905A CN 105771636 B CN105771636 B CN 105771636B
Authority
CN
China
Prior art keywords
mixture
mass ratio
preparation
stirring
mixing
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
CN201610252905.7A
Other languages
Chinese (zh)
Other versions
CN105771636A (en
Inventor
王莉萍
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.)
Beijing Qingxin Environmental Engineering Technology Co ltd
Original Assignee
Yancheng Qingxin Environmental 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 Yancheng Qingxin Environmental Technology Co Ltd filed Critical Yancheng Qingxin Environmental Technology Co Ltd
Priority to CN201810452307.3A priority Critical patent/CN108479373B/en
Priority to CN201610252905.7A priority patent/CN105771636B/en
Priority to CN201810452308.8A priority patent/CN108579358A/en
Publication of CN105771636A publication Critical patent/CN105771636A/en
Application granted granted Critical
Publication of CN105771636B publication Critical patent/CN105771636B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

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
    • B01D53/48Sulfur compounds
    • B01D53/50Sulfur 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
    • B01D53/46Removing components of defined structure
    • B01D53/48Sulfur compounds
    • B01D53/50Sulfur oxides
    • B01D53/508Sulfur oxides by treating the gases with solids
    • 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
    • B01D53/86Catalytic processes
    • B01D53/8603Removing sulfur compounds
    • B01D53/8609Sulfur 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
    • B01D53/02Separation 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 by adsorption, e.g. preparative gas chromatography
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/04Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of alkali metals, alkaline earth metals or magnesium
    • B01J20/043Carbonates or bicarbonates, e.g. limestone, dolomite, aragonite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/10Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
    • B01J20/14Diatomaceous earth
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • B01J20/24Naturally occurring macromolecular compounds, e.g. humic acids or their derivatives
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/002Mixed oxides other than spinels, e.g. perovskite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/02Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the alkali- or alkaline earth metals or beryllium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2253/00Adsorbents used in seperation treatment of gases and vapours
    • B01D2253/10Inorganic adsorbents
    • B01D2253/106Silica or silicates
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2253/00Adsorbents used in seperation treatment of gases and vapours
    • B01D2253/10Inorganic adsorbents
    • B01D2253/106Silica or silicates
    • B01D2253/11Clays
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2253/00Adsorbents used in seperation treatment of gases and vapours
    • B01D2253/25Coated, impregnated or composite adsorbents
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • B01D2258/0283Flue gases
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2523/00Constitutive chemical elements of heterogeneous catalysts

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Analytical Chemistry (AREA)
  • Organic Chemistry (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • General Chemical & Material Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Biomedical Technology (AREA)
  • Health & Medical Sciences (AREA)
  • Materials Engineering (AREA)
  • Inorganic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Geochemistry & Mineralogy (AREA)
  • Treating Waste Gases (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

The invention belongs to environmental technology fields, disclose a kind of preparation method of flue gas desulfurization pulvis, include the following steps:Step 1)Stirring and heating, step 2)Crushing, ball milling and immersion, step 3)Grinding and mixing, step 4)Calcining, step 5)It is mixed.The preparation method of flue gas desulfurization pulvis of the present invention is simple, is suitble to industrialized production.

Description

A kind of preparation method of flue gas desulfurization pulvis
Technical field
The invention belongs to environmental technology fields, disclose a kind of preparation method of flue gas desulfurization pulvis.
Background technology
In recent years, the industrial revolution is grown rapidly, and environmental technology field lags far behind.China is an Industrial Boiler production With use big country, coal-burned industrial boiler situation makes people worried, and Industrial Boiler coal-fired flue-gas in 2010 discharges sulfur dioxide about 1000 Ten thousand tons.Development clean combustion technique is a war of the atmosphere polluting problem based on China's solution primary energy combustion product gases pollution Slightly countermeasure is to realize the important technology direction that economy, social sustainable development and economy, energy environment develop in harmony;Clean combustion The core of technology is the burning of primary energy high cleaning, and the emission reduction that sulphur is a suitable China's national situation is consolidated in wherein primary energy desulfurization SO2One of technical measures.
Under such national conditions, novel desulphurization pulvis is studied, there will be extremely strong vitality, it can be in metallurgical, power generation, water The flue gas desulfurization in the fields such as mud, Industrial Boiler uses, and has popularity, advance and generality.At present, more company opens Begin set about research can simultaneous SO_2 and NO removal preparation, there are also launch sale;There are costs for most of desulfurization preparation Relatively high, adsorbance is smaller, and stability is not high, in large-scale application there are it is certain the defects of.In recent years, in environmental problem And in the case of energy crisis getting worse, both at home and abroad gradually by goal in research be transferred to exploitation it is relatively inexpensive, effective New material prepares desulfurization preparation, such as different kind organism material and mineral material.
Invention content
Invention content
For overcome the deficiencies in the prior art, the present invention provides a kind of preparation method of flue gas desulfurization pulvis, this method Simple possible, the desulfurization powder desulfurization effect of preparation is good, capacity is high, can be applied to various flue gas desulfurizations.
The present invention is realized by following scheme:
A kind of preparation method of flue gas desulfurization pulvis, includes the following steps:
Step 1)Stirring and heating, step 2)Crushing, ball milling and immersion, step 3)Grinding and mixing, step 4)Calcining, step Rapid 5)It is mixed;
Specifically, include the following steps:
Step 1)Stirring and heating:Calcium oxide, activated carbon, calcirm-fluoride and dicalcium silicate are added to mixing agitator In, 500 turns/min stirring 6min spray soya-bean oil, after stirring, are heated to 80 DEG C, keep the temperature 3min, mixed while stirring Expect A;Wherein, the mass ratio of activated carbon, calcium oxide, calcirm-fluoride, dicalcium silicate and soya-bean oil is 15:10:3:3:1;
Step 2)Crushing, ball milling and immersion:Monticellite, mullite and shepardite are used into crusher in crushing respectively, Then it mixes, then puts into vibrator, grain size to be milled to is 100-200um, stops ball milling, discharging, then with dense It spends and is impregnated 6 hours for the sodium hydrate aqueous solution of 1M, last 50 DEG C of drying obtain mixture B;Wherein, monticellite, Mo Lai The mass ratio of stone, shepardite and sodium hydrate aqueous solution is 3:2:2:5;
Step 3)Grinding and mixing:Soybean stalk with pulverizer is crushed, is then ground to the powder of 300-500um, most It is mixed afterwards with nano silicon dioxide, obtains mixture C;Wherein, the mass ratio of soybean stalk and nano silicon dioxide is 5:1;
Step 4)Calcining:By dolomite and diatomite according to 2:1 mass ratio mixing, is subsequently placed in and is calcined in calcining furnace 2h, calcination temperature are 1000 DEG C, take out, are cooled to room temperature, crushing obtains mixture D;
Step 5)It is mixed:By mixture A, mixture B, mixture C and mixture D according to 15-25:10-15:4- 7:The mass ratio of 2-3 be mixed evenly to get.
Preferably, the grain size of nano silicon dioxide is 200-500nm.
The advantageous effect that the present invention obtains mainly includes the following aspects:
The preparation method of flue gas desulfurization pulvis of the present invention is simple, is suitble to industrialized production, low raw-material cost, the powder of preparation Agent is environment friendly and pollution-free, can be widely applied to all kinds of flue gas desulfurizations.
Pulvis material combination prepared by the present invention is reasonable, and desulfurization effect is good, and sulfur capacity is high, shortens the vulcanization reaction time.
The present invention is mostly using the raw material and agricultural wastes derived from a wealth of sources so that waste becomes the new energy, solves Environmental protection of enterprise pressure, realizing turns waste into wealth.
The present invention is increased adsorption effect, is played good catalytic action using dolime and diatomaceous technique.
Present invention employs discarded soybean stalks, and grain size is big, form certain pore structure, improve adsorption effect.
The present invention is by spraying soya-bean oil and heating so that pulvis surface forms protective film, improves the holding time of pulvis And desulfuration efficiency.
The present invention improves dispersion effect, expands adsorbent capacity by adding nanometer particle.
Specific embodiment
In order to make those skilled in the art better understand the technical solutions in the application, have below in conjunction with the application Body embodiment more clearly and completely describes the present invention, it is clear that described embodiment is only the application one Divide embodiment, instead of all the embodiments.Based on the embodiment in the application, those of ordinary skill in the art are not making All other embodiments obtained under the premise of creative work should all belong to the scope of protection of the invention.
Embodiment 1
A kind of preparation method of flue gas desulfurization pulvis, includes the following steps:
Step 1)Stirring and heating, step 2)Crushing, ball milling and immersion, step 3)Grinding and mixing, step 4)Calcining, step Rapid 5)It is mixed;
Specifically, include the following steps:
Step 1)Stirring and heating:Calcium oxide, activated carbon, calcirm-fluoride and dicalcium silicate are added to mixing agitator In, 500 turns/min stirring 6min spray soya-bean oil, after stirring, are heated to 80 DEG C, keep the temperature 3min, mixed while stirring Expect A;Wherein, the mass ratio of activated carbon, calcium oxide, calcirm-fluoride, dicalcium silicate and soya-bean oil is 15:10:3:3:1;
Step 2)Crushing, ball milling and immersion:Monticellite, mullite and shepardite are used into crusher in crushing respectively, Then it mixes, then puts into vibrator, grain size to be milled to is 100um, stops ball milling, discharging, then with a concentration of The sodium hydrate aqueous solution of 1M impregnates 6 hours, and last 50 DEG C of drying obtain mixture B;Wherein, monticellite, mullite, The mass ratio of shepardite and sodium hydrate aqueous solution is 3:2:2:5;
Step 3)Grinding and mixing:Soybean stalk with pulverizer is crushed, is then ground to the powder of 300um, finally with Nano silicon dioxide mixes, and obtains mixture C;Wherein, the mass ratio of soybean stalk and nano silicon dioxide is 5:1;
Step 4)Calcining:By dolomite and diatomite according to 2:1 mass ratio mixing, is subsequently placed in and is calcined in calcining furnace 2h, calcination temperature are 1000 DEG C, take out, are cooled to room temperature, crushing obtains mixture D;
Step 5)It is mixed:By mixture A, mixture B, mixture C and mixture D according to 15:10:4:2 matter Amount than be mixed evenly to get.
Wherein, the grain size of nano silicon dioxide is 200nm.
Embodiment 2
A kind of preparation method of flue gas desulfurization pulvis, includes the following steps:
Step 1)Stirring and heating, step 2)Crushing, ball milling and immersion, step 3)Grinding and mixing, step 4)Calcining, step Rapid 5)It is mixed;
Specifically, include the following steps:
Step 1)Stirring and heating:Calcium oxide, activated carbon, calcirm-fluoride and dicalcium silicate are added to mixing agitator In, 500 turns/min stirring 6min spray soya-bean oil, after stirring, are heated to 80 DEG C, keep the temperature 3min, mixed while stirring Expect A;Wherein, the mass ratio of activated carbon, calcium oxide, calcirm-fluoride, dicalcium silicate and soya-bean oil is 15:10:3:3:1;
Step 2)Crushing, ball milling and immersion:Monticellite, mullite and shepardite are used into crusher in crushing respectively, Then it mixes, then puts into vibrator, grain size to be milled to is 200um, stops ball milling, discharging, then with a concentration of The sodium hydrate aqueous solution of 1M impregnates 6 hours, and last 50 DEG C of drying obtain mixture B;Wherein, monticellite, mullite, The mass ratio of shepardite and sodium hydrate aqueous solution is 3:2:2:5;
Step 3)Grinding and mixing:Soybean stalk with pulverizer is crushed, is then ground to the powder of 500um, finally with Nano silicon dioxide mixes, and obtains mixture C;Wherein, the mass ratio of soybean stalk and nano silicon dioxide is 5:1;
Step 4)Calcining:By dolomite and diatomite according to 2:1 mass ratio mixing, is subsequently placed in and is calcined in calcining furnace 2h, calcination temperature are 1000 DEG C, take out, are cooled to room temperature, crushing obtains mixture D;
Step 5)It is mixed:By mixture A, mixture B, mixture C and mixture D according to 25:15:7:3 matter Amount than be mixed evenly to get.
Wherein, the grain size of nano silicon dioxide is 500nm.
Embodiment 3
The flue gas containing sulfur dioxide is simulated, into the desulphurization reaction room of the desulfurization powder prepared containing embodiment 2, flue gas speed Spend for 0.5m/min, flue-gas temperature is 100 DEG C, be set separately desulfurization time for 10,20,30,60min, measure desulfurization degree, specifically It is shown in Table 1:
Table 1
Desulfurization time min Inlet concentration mg/m3 Exit concentration mg/m3 Desulfurization degree %
10 748.5 189.3 74.71
20 761.3 167.6 77.99
30 759.1 133.5 82.41
60 753.8 129.6 82.81
Conclusion:Inventive desulfurization powder desulfurization rate can reach more than 80%;After reaction, desulfurization powder work is had detected 30min is to the adsorbance of sulfur dioxide:The adsorbable sulfur dioxide 58.7mg of every gram of adsorbent, adsorption capacity is good, and the reaction time is short.
Above in association with specific embodiment, invention has been described, it will be appreciated by those skilled in the art that this A little descriptions are all exemplary, and are not limiting the scope of the invention.Those skilled in the art can be according to the present invention Spirit and principle various variants and modifications are made to the present invention, these variants and modifications are also within the scope of the invention.

Claims (2)

1. a kind of preparation method of flue gas desulfurization pulvis, which is characterized in that the preparation method includes the following steps:
Step 1)Stirring and heating:Calcium oxide, activated carbon, calcirm-fluoride and dicalcium silicate are added in mixing agitator, 500 Turn/min stirring 6min, spray soya-bean oil while stirring, after stirring, be heated to 80 DEG C, keep the temperature 3min, obtain mixture A;Its In, activated carbon, calcium oxide, calcirm-fluoride, dicalcium silicate and soya-bean oil mass ratio be 15:10:3:3:1;
Step 2)Crushing, ball milling and immersion:Monticellite, mullite and shepardite are used into crusher in crushing respectively, then Mixing, then put into vibrator, grain size to be milled to is 100-200um, stops ball milling, discharging, then with a concentration of The sodium hydrate aqueous solution of 1M impregnates 6 hours, and last 50 DEG C of drying obtain mixture B;Wherein, monticellite, mullite, The mass ratio of shepardite and sodium hydrate aqueous solution is 3:2:2:5;
Step 3)Grinding and mixing:Soybean stalk with pulverizer is crushed, is then ground to the powder of 300-500um, finally with Nano silicon dioxide mixes, and obtains mixture C;Wherein, the mass ratio of soybean stalk and nano silicon dioxide is 5:1;
Step 4)Calcining:By dolomite and diatomite according to 2:1 mass ratio mixing, is subsequently placed in calcining furnace and calcines 2h, Calcination temperature is 1000 DEG C, takes out, is cooled to room temperature, and crushing obtains mixture D;
Step 5)It is mixed:By mixture A, mixture B, mixture C and mixture D according to 15-25:10-15:4-7:2- 3 mass ratio be mixed evenly to get.
2. preparation method according to claim 1, which is characterized in that the grain size of the nano silicon dioxide is 200- 500nm。
CN201610252905.7A 2016-04-22 2016-04-22 A kind of preparation method of flue gas desulfurization pulvis Active CN105771636B (en)

Priority Applications (3)

Application Number Priority Date Filing Date Title
CN201810452307.3A CN108479373B (en) 2016-04-22 2016-04-22 Preparation method of environment-friendly flue gas desulfurization powder
CN201610252905.7A CN105771636B (en) 2016-04-22 2016-04-22 A kind of preparation method of flue gas desulfurization pulvis
CN201810452308.8A CN108579358A (en) 2016-04-22 2016-04-22 A kind of preparation method of high-efficiency flue gas desulfurization pulvis

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610252905.7A CN105771636B (en) 2016-04-22 2016-04-22 A kind of preparation method of flue gas desulfurization pulvis

Related Child Applications (2)

Application Number Title Priority Date Filing Date
CN201810452308.8A Division CN108579358A (en) 2016-04-22 2016-04-22 A kind of preparation method of high-efficiency flue gas desulfurization pulvis
CN201810452307.3A Division CN108479373B (en) 2016-04-22 2016-04-22 Preparation method of environment-friendly flue gas desulfurization powder

Publications (2)

Publication Number Publication Date
CN105771636A CN105771636A (en) 2016-07-20
CN105771636B true CN105771636B (en) 2018-07-06

Family

ID=56398121

Family Applications (3)

Application Number Title Priority Date Filing Date
CN201810452307.3A Active CN108479373B (en) 2016-04-22 2016-04-22 Preparation method of environment-friendly flue gas desulfurization powder
CN201610252905.7A Active CN105771636B (en) 2016-04-22 2016-04-22 A kind of preparation method of flue gas desulfurization pulvis
CN201810452308.8A Withdrawn CN108579358A (en) 2016-04-22 2016-04-22 A kind of preparation method of high-efficiency flue gas desulfurization pulvis

Family Applications Before (1)

Application Number Title Priority Date Filing Date
CN201810452307.3A Active CN108479373B (en) 2016-04-22 2016-04-22 Preparation method of environment-friendly flue gas desulfurization powder

Family Applications After (1)

Application Number Title Priority Date Filing Date
CN201810452308.8A Withdrawn CN108579358A (en) 2016-04-22 2016-04-22 A kind of preparation method of high-efficiency flue gas desulfurization pulvis

Country Status (1)

Country Link
CN (3) CN108479373B (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111672269A (en) * 2020-06-28 2020-09-18 潮州市中乾环境科技有限公司 Environment-friendly waste gas treatment device with adsorption function
CN112875738A (en) * 2021-02-01 2021-06-01 大冶市鑫鼎实业有限公司 Process for refining dolomite purity by decomposition and desulfurization

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0299137A (en) * 1988-10-05 1990-04-11 Mitsubishi Heavy Ind Ltd Desulfurizing agent
CN101074402A (en) * 2006-05-17 2007-11-21 陈钧 Efficient sulfur-fixing agent and its usage
CN103495403A (en) * 2013-08-30 2014-01-08 蚌埠首创滤清器有限公司 Modified activated carbon adsorption desulfurization agent and its preparation method
CN103566880A (en) * 2013-09-29 2014-02-12 安徽金叶炭素科技有限公司 Rice hull modified active carbon adsorption desulfurizing agent and preparation method thereof
CN103566879A (en) * 2013-09-26 2014-02-12 蚌埠华纺滤材有限公司 Expanded perlite modified activated carbon automobile exhaust desulfurizing agent, and preparation method thereof
CN104479792A (en) * 2014-12-29 2015-04-01 李康 Preparation method for desulfurizing agent for boiler coal combustion

Family Cites Families (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3634795B2 (en) * 2001-11-29 2005-03-30 株式会社日本触媒 Nitrogen oxide and / or sulfur oxide adsorbent
CN101870900B (en) * 2010-06-29 2013-09-18 臧鑫 Desulphurizing powder produced by using alkaline residue and production process thereof
CN103127908B (en) * 2012-12-13 2015-08-19 青岛特利尔环保锅炉工程有限公司 The method of preparation and use of boiler tail flue gas desulphurization denitration purification thing
CN104475050A (en) * 2014-11-13 2015-04-01 安徽凤凰滤清器股份有限公司 Activated carbon diatomite particles capable of rapid purification of flue gas and preparation method thereof
CN105327613B (en) * 2015-10-27 2017-09-29 西安建筑科技大学 A kind of desulfurizing agent and its application

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0299137A (en) * 1988-10-05 1990-04-11 Mitsubishi Heavy Ind Ltd Desulfurizing agent
CN101074402A (en) * 2006-05-17 2007-11-21 陈钧 Efficient sulfur-fixing agent and its usage
CN103495403A (en) * 2013-08-30 2014-01-08 蚌埠首创滤清器有限公司 Modified activated carbon adsorption desulfurization agent and its preparation method
CN103566879A (en) * 2013-09-26 2014-02-12 蚌埠华纺滤材有限公司 Expanded perlite modified activated carbon automobile exhaust desulfurizing agent, and preparation method thereof
CN103566880A (en) * 2013-09-29 2014-02-12 安徽金叶炭素科技有限公司 Rice hull modified active carbon adsorption desulfurizing agent and preparation method thereof
CN104479792A (en) * 2014-12-29 2015-04-01 李康 Preparation method for desulfurizing agent for boiler coal combustion

Also Published As

Publication number Publication date
CN108479373B (en) 2021-03-05
CN108479373A (en) 2018-09-04
CN108579358A (en) 2018-09-28
CN105771636A (en) 2016-07-20

Similar Documents

Publication Publication Date Title
CN105597701B (en) A kind of adsorbent for handling boiler smoke
CN103566903B (en) A kind of Concave-convex clay rod modified activated carbon and preparation method thereof
CN104289195B (en) A kind of activated carbon diatomite particle of hole prosperity low cost and preparation method thereof
CN101177264A (en) Method for combined production of activative carbon, white carbon black and soda by employing biomass power plant waste
CN101560110B (en) Spherical light porous material for wastewater treatment
CN103586011B (en) Sintering-free forming and coating method of MIL-101 material with ultrahigh specific surface area
CN105771636B (en) A kind of preparation method of flue gas desulfurization pulvis
CN106000073B (en) A kind of environment-protective process for administering boiler smoke
CN105749866B (en) A kind of composite desulfurization powder and its application
CN108114974A (en) A kind of method for repairing cadmium-polycyclic aromatic hydrocarbon composite pollution soil
CN114229852A (en) Method for removing SO in flue gas by using steel slag2Method for synergistically extracting silica gel
CN105854831B (en) A kind of compound of calcium carbonate of desulphurization denitration
CN104437399A (en) Low-cost activated carbon kieselguhr particles with developed pores, and preparation method of kieselguhr particles
CN203944281U (en) Flue gas desulfur device
CN103566877A (en) Modified active carbon capable of absorbing electromagnetic waves and preparation method thereof
CN105688849B (en) A kind of multi-functional desulphurization denitration environmental protection preparation and preparation method thereof
CN107628619A (en) A kind of preparation method of the rich nitrogen active sludge carbon of adulterated food leftover bits and pieces
CN110624496B (en) Preparation method of porous boron nitride-based composite material for purifying organic wastewater
CN105854506B (en) A kind of new process of boiler flue gas desulfurization denitration
CN103357376A (en) Nano-grade attapulgite substrate SO2 absorption agent preparation method
CN106268660A (en) A kind of modified adsorbent for absorbing carbon dioxide
CN105903323B (en) A kind of solid-state desulfurization powder and its preparation process
CN105664705A (en) Limestone and attapulgite mixed desulfurizing agent
CN111821942A (en) High-efficiency dioxin adsorbent for waste incineration and preparation method and application thereof
CN106237999B (en) A kind of preparation process of carbon dioxide absorber

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
TA01 Transfer of patent application right
TA01 Transfer of patent application right

Effective date of registration: 20180524

Address after: 224001 Jiangsu Yancheng City Ting Lake District Nanyang Town, south of photovoltaic Road, six road east 1 buildings 728 rooms (8)

Applicant after: YANCHENG QINGXIN ENVIRONMENTAL TECHNOLOGY Co.,Ltd.

Address before: 311411 Shang Sha Village, Chang Kou Town, Fuyang District, Hangzhou, Zhejiang

Applicant before: HANGZHOU FUYANG GAOBO INFORMATION TECHNOLOGY SERVICE Co.,Ltd.

GR01 Patent grant
GR01 Patent grant
TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20220826

Address after: 101405 Beijing city Huairou District Bohai town Huai Sha Road No. 536

Patentee after: Beijing Qingxin Environmental Engineering Technology Co.,Ltd.

Address before: 224001 Jiangsu Yancheng City Ting Lake District Nanyang Town, south of photovoltaic Road, six road east 1 buildings 728 rooms (8)

Patentee before: YANCHENG QINGXIN ENVIRONMENTAL TECHNOLOGY Co.,Ltd.