CN108926911A - A kind of preparation method of denitration demercuration monoblock type filtrate - Google Patents

A kind of preparation method of denitration demercuration monoblock type filtrate Download PDF

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CN108926911A
CN108926911A CN201810666836.3A CN201810666836A CN108926911A CN 108926911 A CN108926911 A CN 108926911A CN 201810666836 A CN201810666836 A CN 201810666836A CN 108926911 A CN108926911 A CN 108926911A
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salt
monoblock type
denitration demercuration
preparation
filtrate
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CN108926911B (en
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陈建军
单良
李俊华
王慧
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Yancheng Environmental Engineering Technology Research And Development Center Tsinghua University
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Yancheng Environmental Engineering Technology Research And Development Center Tsinghua University
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D39/00Filtering material for liquid or gaseous fluids
    • B01D39/14Other self-supporting filtering material ; Other filtering material
    • B01D39/20Other self-supporting filtering material ; Other filtering material of inorganic material, e.g. asbestos paper, metallic filtering material of non-woven wires
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D46/00Filters or filtering processes specially modified for separating dispersed particles from gases or vapours
    • B01D46/30Particle separators, e.g. dust precipitators, using loose filtering material
    • 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
    • B01D53/8621Removing nitrogen compounds
    • B01D53/8625Nitrogen oxides
    • B01D53/8628Processes characterised by a specific catalyst
    • 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
    • B01D53/8665Removing heavy metals or compounds thereof, e.g. mercury
    • 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
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/76Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/84Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/889Manganese, technetium or rhenium
    • B01J23/8892Manganese
    • B01J35/50

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Environmental & Geological Engineering (AREA)
  • Biomedical Technology (AREA)
  • Health & Medical Sciences (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Geology (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Catalysts (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Abstract

The invention discloses a kind of preparation methods of denitration demercuration monoblock type filtrate, it comprises the steps of: and pretreated metal fiber felt is impregnated in metal salt precursor solution, then grown not only in metal fiber felt surface in situ with denitration demercuration catalysis but also the multi-functional monoblock type filtrate of dust removal through the processes such as hydro-thermal and high-temperature calcination.Denitration demercuration dedusting multifunctional composite filter material prepared by the present invention not only can be avoided fly ash granule to the adverse effect of catalyst, can also effective emission reduction fine dust;And catalyst is firmly combined with filtrate, the proper property of filtrate is not influenced, particularly suitable for industrialized production.

Description

A kind of preparation method of denitration demercuration monoblock type filtrate
Technical field
The present invention relates to a kind of preparation methods of denitration demercuration monoblock type filtrate, belong to combined type filtrate technical field.
Background technique
Nitrogen oxides (NOX) in atmosphere is mainly derived from steel, cement, glass-ceramic, coal-burning power plant, waste incineration etc. The flue gas given off easily causes the atmosphere pollution phenomenon such as haze, photochemical fog, acid rain.In addition, the mercury in industrial smoke is also It is Environmental Pollution object, the discharge of category coal-burning power plant is the most serious, and the coal fire discharged mercury into atmosphere mainly has Elemental Mercury (Hg0), bivalent mercury (Hg2+), granular absorption mercury (Hgp).It wherein, can be by Hg by the processes such as wet desulphurization and dedusting2+With Hgp Effectively removing, but Hg0 free property is strong, solubility is low in water, it is difficult to remove, most easily cause atmosphere mercury pollution.In addition, dust is outstanding It is that suspension time is long in an atmosphere for PM10 fine particle below, causes easily to reduce atmospheric visibility, it is normal to influence the mankind Life and production activity, particle dust, which enters human lung, can also cause toxic pneumonitis or silicosis.In short, above-mentioned environment is dirty Dye object has become the Social Events of relationship people production and living health, conservation culture and sustainable development, reduces nitrogen oxidation The discharge amount of object, Elemental Mercury, dust has great importance for alleviating, improving environmental problem.
Currently, the removal for nitrogen oxides, mainly uses NH3-SCR method, wherein V2O5-WO3/TiO2 catalyst is wide General application, still, high-temperature area of the operation temperature window at 300-400 DEG C, and V is volatile.In addition, if demercuration is using absorption When mode, the absorption of mercury is closely related with temperature, and flue-gas temperature is higher, and the adsorbing and removing efficiency of mercury is often lower, thus high temperature Gaseous elemental mercury is difficult to effectively remove in flue gas.Field is post-processed in industrial smoke, sack cleaner is due to high dust collection efficiency, fortune The features such as row stability is good, is easily recycled has been widely used in the fields such as coal-burning power plant, waste incineration, cement.Wherein, filtrate It is the core of sack cleaner, such as: glass fibre, PTFE.The use temperature (150-200 DEG C or so) of conventional cloth bag filtrate, Well below the temperature of catalysis reaction, which has limited the development with denitration demercuration multifunctional filter material.If using non-vanadium denitration It cooperates with demercuration catalyst and dedusting filtrate compound, realizes that multi-pollutant cooperation-removal then can effectively avoid the above problem.
Since the variable valency metals oxide such as MnOx, CeOX, FeOX, CoOX has a variety of valence states, free oxygen vacancies abundant, Thus have many advantages, such as good low-temperature catalytic activity, while because its is resourceful, inexpensive, environment-protecting and non-poisonous, having become research Hot spot.Such as: after the metal salt solution of Mn, Ce, Zr are impregnated in filter media fibre by patent (CN107158799A), then using alkaline solution Aging process is carried out to it, dedusting denitration composite filtering material fiber, but the easy powder of detached of filtrate of this support type is obtained, influences to remove Dirt denitration effect.Patent (CN104014200A) is by denitrating catalyst, polytetrafluoroethylene (PTFE) powder, diffusant, coupling agent, lubricant It is uniformly mixed according to a certain percentage and catalysis filter membrane is made dust removal integrated filtrate is made by hot pressing complex method, although this method The binding strength of catalyst and filtrate is strengthened, but overlay film hinders the active site exposure of catalyst, catalyst utilization It is low, the problems such as causing catalytic activity and low efficiency.Thus, denitration demercuration catalyst and dedusting filtrate are coupled in a body technique extremely The present is still a major challenge.
Summary of the invention
The technical problem to be solved by the invention is to provide one kind to have denitration demercuration dedusting Trinitarian multi-functional multiple The preparation method for closing filtrate, further provide a kind of good mechanical property, be firmly combined, thermal stability it is good and simple and easy The preparation method of composite filtering material.
In order to solve the above technical problems, the technical solution adopted by the present invention are as follows:
A kind of preparation method of denitration demercuration monoblock type filtrate, comprising the following steps:
(1) pretreatment of metal fiber felt is made into fragment shape, removes the metal fiber felt surface and oil contaminant and oxide, It is rinsed with deionized water, it is spare after dry;
(2) mixed solution of divalent metal salt and trivalent metal salt is prepared in the preparation of monoblock type filtrate, and wherein divalent metal salt is molten Liquid concentration is 0.0625 ~ 0.5mol/L, and trivalent metal concentration of salt solution is 0.0125 ~ 0.18mol/L, with catalyst loadings 20-80g/m2Meter, takes metal fiber felt described in appropriate step (1) to be put into mixing salt solution, is adjusted using in-situ deposition agent Solution ph is 8.5-10.5, is transferred in reaction kettle, under the conditions of 50 ~ 200 DEG C react 6 ~ for 24 hours, be cooled to room temperature, wash, It is dry, above-mentioned product is calcined to 2 ~ 6h at 350 ~ 550 DEG C to get the filtrate.
The additional amount of metal fiber felt is related with the active component coverage condition of obtained filter material surface, using beyond above-mentioned Reunion or very few occurs for the active component that the additional amount of range may result in filter material surface load, to cannot achieve activity The uniform load of component influences the denitration demercuration performance of filtrate;
The height of concentration of metal ions influences the hydrolysis situation of ion, then influences metal composite oxide pattern;
The adjusting of solution ph is too low or excessively high, is all unfavorable for metal ion in the deposition growing on metal fiber felt surface;
Hydrothermal temperature is excessively high, overlong time, then is unfavorable for the holding of porous nanometer structure, influences the stability of catalyst;Temperature Too low, the hydro-thermal time is too short, will lead to that aluminium, cobalt, the hydrolysis of manganese ion and settling velocity are too slow, and crystal growth is incomplete;
Calcination temperature is higher than above-mentioned section or calcination temperature is too long, will lead to the collapsing of three-dimensional porous structure, is lower than the section Or calcination time is too short, can draw that metal oxide crystallinity is big, these will affect the ratio of the metal composite oxide filtrate Surface area, crystalline structure and cellular structure etc., and then influence denitration demercuration activity.
The metal fiber felt includes stainless steel fibre felt, iron-chromium-aluminum felt, nickel fibre felt or alumina silicate fiber felt.
The cobalt salt is one of cobaltous sulfate, cobalt nitrate, cobalt chloride or cobalt acetate, manganese salt be potassium permanganate, manganese sulfate, One of manganese nitrate, manganese chloride or manganese acetate, aluminium salt are one of aluminium chloride, aluminum sulfate or aluminum nitrate.Different type Close object in ion hydrolytic precipitation ability difference may cause filter material surface formation metal oxide crystal form, grain size and Crystallinity is different, to influence the activity of its denitration demercuration.
The in-situ deposition agent be ammonium hydroxide, sodium hydroxide, sodium carbonate, hexamethylenetetramine, urea, ammonium carbonate, ammonium chloride, One of ammonium fluoride, ammonium hydrogen carbonate are a variety of.Different deposition agents directly affects the metal front for being supported on fibrofelt surface The type and pattern of body, to influence catalyst effect.
The disk for using impact style that diameter is made as 3cm in the metal fiber felt in step (1).
Supersound washing is carried out to the metal fiber felt using ethyl alcohol and hydrochloric acid in step (1).
Advantageous effects of the invention:
(1) catalyst is compared using metal fiber felt as carrier compared with carriers such as traditional glass mat, PPS fibrofelts, resistance to High temperature, corrosion-resistant, three-dimensional porous structure, heat conduction efficiency are high, can be to avoid the effective active component group of sintering under high temperature environment Poly-, porosity height, large specific surface area, the features such as size distribution is uniform, filtering accuracy is high, are conducive to catalyst on its surface Uniform load coupling, metallic atom and metallic fiber form strong interaction, not easily to fall off and have stable denitration demercuration Efficiency.
(2) catalyst has three-dimensional hierarchical structure, and orderly metal nano chip arrays are coupled in metal fiber felt in situ Air resistance is reduced on surface, and raising active component is evenly dispersed, improves unit area catalyst utilization, avoids traditional The insufficient problem of active site exposure of coated filter material containing catalyst.
(3) the denitration demercuration integration filtrate active component is the composite oxides for including divalent metal and trivalent metal, By synergic catalytic effect, good low-temperature denitration activity and demercuration efficiency are presented, and there are good dust removing effects.
(4) catalyst is simple and easy by hydro-thermal and the preparation for calcining two-step method.Catalyst is raw in situ in filter material surface It is long, it is not necessarily to post forming, production technology and cost can be simplified, and is avoided that the secondary pollution that binder generates in tradition coating.
Detailed description of the invention
Fig. 1 is filtrate of the present invention at different temperatures de- of filtrate prepared by embodiment 3 in no hydrogen chloride Mercury rate;
Fig. 2 is filtrate prepared by the present invention electronic image under the microscope.
Specific embodiment
The invention will be further described below in conjunction with the accompanying drawings.Following embodiment is only used for clearly illustrating the present invention Technical solution, and not intended to limit the protection scope of the present invention.
Embodiment 1:
Stainless steel fibre felt is washed into the disk that diameter is 3 cm, 3 disks is taken to be surpassed respectively by the hydrochloric acid of ethyl alcohol and 1 mmol/L Sound washs 1 h, removes surface and oil contaminant and oxide, is then rinsed by deionized water, dry at 60 DEG C;
Mn (NO is weighed first3)2(5mmol) and Al (NO3)3.9H2O(2mmol it) is dissolved in the deionized water of 80 ml, is stirred strongly It mixes to being completely dissolved to form solution A, 25% ammonium hydroxide is slowly added dropwise in solution A, it is molten to 8.5 ± 0.2 stirrings to adjust pH value Solution forms suspension, is transferred in the reaction kettle of 100ml, is put into baking oven, and reaction temperature control is 100 DEG C, and the reaction time is For 24 hours, reaction end is taken out reaction kettle and is cooled to room temperature, and sediment is taken out, with deionized water and each centrifuge washing 3 of dehydrated alcohol It is secondary, 80 DEG C of dry 12h.Obtain presoma Co3-xMnxAl-LDHs;By above-mentioned product 400o2 h are calcined in C air, and institute is made The denitration demercuration monoblock type filtrate stated.
On the stainless steel fixed bed denitration demercuration reactor of laboratory to the catalysis filtrate prepared in above-mentioned case study on implementation into Row test, test filtrate quality be 3g, denitration demercuration test condition: 50-300 DEG C of reaction temperature, air speed 20000h-1, NH3 concentration 500ppm, NO concentration 500ppm, 5ppmHCl, O2Concentration 5%, N2For Balance Air, following embodiment is tested with embodiment 1.
The denitration demercuration test of 1 embodiment 1 of table at different temperatures
Removal efficiency (%) 50℃ 100℃ 150℃ 200℃ 250℃ 300℃
Denitrification rate 20.2 42.6 65.3 82.3 83.8 75.1
Demercuration rate 30.1 72.5 83.2 84.7 82.5 82.3
Embodiment 2:
Nickel fibre felt is washed into the disk that diameter is 3 cm, takes 3 disks respectively by the hydrochloric ultrasonic wave of ethyl alcohol and 1 mmol/L 1 h is washed, surface and oil contaminant and oxide is removed, is then rinsed by deionized water, 60oIt is dry under C;
Co (NO is weighed first3)2.6H2O(8 mmol), 50% Mn (NO3)2(15mmol) and Al (NO3)3.9H2O(7 mmol) It is dissolved in the deionized water of 75ml, strong stirring to form solution A to being completely dissolved, by 2mol/L sodium hydroxide, sodium carbonate liquor It is slowly added dropwise in solution A, adjusts pH value to 9.5 ± 0.2 stirring and dissolvings and form suspension B, suspension B is transferred to In the reaction kettle of 100ml, it is put into baking oven, reaction temperature control is 150 DEG C, and the reaction time is 12 h, and reaction terminates to take out reaction Kettle is cooled to room temperature, and sediment is taken out, with deionized water and each centrifuge washing of dehydrated alcohol 3 times, 80 DEG C of dry 12h.Before obtaining Drive body Co3-xMnxAl-LDHs;By above-mentioned product 300o2 h are calcined in C air, and the denitration demercuration monoblock type filter is made Material.
The denitration demercuration test of 2 embodiment 2 of table at different temperatures
Removal efficiency (%) 50℃ 100℃ 150℃ 200℃ 250℃ 300℃
Denitrification rate 25.5 50.6 75.8 92.3 90.6 85.2
Demercuration rate 35.4 82.5 88.9 90.2 89.5 85.6
Embodiment 3:
Iron-chromium-aluminum felt is washed into the disk that diameter is 3 cm, takes 3 disks respectively by the hydrochloric acid of ethyl alcohol and 1 mmol/L 1 h of supersound washing removes surface and oil contaminant and oxide, is then rinsed by deionized water, 60oIt is dry under C;
Co (NO is weighed first3)2.6H2O(10 mmol), 50% Mn (NO3)2(20mmol) and Al (NO3)3.9H2O(10 Mmol it) is dissolved in the deionized water of 60 ml, strong stirring to form solution A to being completely dissolved, and 25% ammonium hydroxide is slowly added dropwise Into solution A, adjusts pH value to 10.5 ± 0.2 stirring and dissolvings and form suspension B, suspension B is transferred to the reaction kettle of 100ml In, it is put into baking oven, reaction temperature control is 200 DEG C, and the reaction time is 8 h, and reaction end is taken out reaction kettle and is cooled to room temperature, takes Sediment out, with deionized water and each centrifuge washing of dehydrated alcohol 3 times, 80 DEG C of dry 12h.Obtain presoma Co3-xMnxAl- LDHs;By above-mentioned product 400o3 h are calcined in C air, and the tool denitration demercuration monoblock type filtrate is made.
The denitration demercuration test of 3 embodiment 3 of table at different temperatures
Removal efficiency (%) 50℃ 100℃ 150℃ 200℃ 250℃ 300℃
Denitrification rate 29.2 54.5 78.9 92.3 90.5 84.1
Demercuration rate 38.1 84.5 88.5 90.7 90.5 87.3
Embodiment 4:
Iron-chromium-aluminum felt is washed into the disk that diameter is 3 cm, takes 3 disks respectively by the hydrochloric acid of ethyl alcohol and 1 mmol/L 1 h of supersound washing removes surface and oil contaminant and oxide, is then rinsed by deionized water, 60oIt is dry under C;
Ni (NO is weighed first3)2.6H2O(10 mmol), 50% Mn (NO3)2(20mmol) and Fe (NO3)3.9H2O(10 Mmol it) is dissolved in the deionized water of 60 ml, strong stirring to form solution A to being completely dissolved, by 2mol/L sodium hydroxide, carbonic acid Sodium solution is slowly added dropwise in solution A, is adjusted pH value to 10.5 ± 0.2 stirring and dissolvings and is formed suspension B, suspension B is turned It moves in the reaction kettle of 100ml, is put into baking oven, reaction temperature control is 200 DEG C, and the reaction time is 8 h, and reaction terminates to take out anti- It answers kettle to be cooled to room temperature, sediment is taken out, with deionized water and each centrifuge washing of dehydrated alcohol 3 times, 80 DEG C of dry 12h.It obtains Presoma Ni3-xMnxFe-LDHs;By above-mentioned product 400o3 h are calcined in C air, the tool denitration demercuration for being made described is whole Formula filtrate.
The denitration demercuration test of 4 embodiment 4 of table at different temperatures
Removal efficiency (%) 50℃ 100℃ 150℃ 200℃ 250℃ 300℃
Denitrification rate 17.2 38.3 52.5 72.8 80.7 69.1
Demercuration rate 25.3 60.5 73.4 74.7 72.5 70.3
The above is only a preferred embodiment of the present invention, it is noted that those skilled in the art are come It says, without departing from the technical principles of the invention, several improvement and deformations can also be made, these improvement and deformations are also answered It is considered as protection scope of the present invention.

Claims (7)

1. a kind of preparation method of denitration demercuration monoblock type filtrate, characterized in that the following steps are included:
(1) pretreatment of metal fiber felt is made into fragment shape, removes the metal fiber felt surface and oil contaminant and oxide, It is rinsed with deionized water, it is spare after dry;
(2) mixed solution of divalent metal salt and trivalent metal salt is prepared in the preparation of monoblock type filtrate, and wherein divalent metal salt is molten Liquid concentration is 0.0625 ~ 0.5mol/L, and trivalent metal concentration of salt solution is 0.0125 ~ 0.18mol/L, with catalyst loadings 20-80g/m2Meter, takes metal fiber felt described in appropriate step (1) to be put into mixing salt solution, is adjusted using in-situ deposition agent Solution ph is 8.5-10.5, is transferred in reaction kettle, under the conditions of 50 ~ 200 DEG C react 6 ~ for 24 hours, be cooled to room temperature, wash, It is dry, above-mentioned product is calcined to 2 ~ 6h at 350 ~ 550 DEG C to get the filtrate.
2. a kind of preparation method of denitration demercuration monoblock type filtrate according to claim 1, characterized in that the divalent gold Belonging to salt includes one or both of cobalt salt, nickel salt, manganese salt, magnesium salts, zinc salt or cerium salt, the trivalent metal salt include aluminium salt or Molysite.
3. a kind of preparation method of denitration demercuration monoblock type filtrate according to claim 1, characterized in that the metal is fine Tieing up felt includes stainless steel fibre felt, iron-chromium-aluminum felt, nickel fibre felt or alumina silicate fiber felt.
4. a kind of preparation method of denitration demercuration monoblock type filtrate according to claim 1, characterized in that metal salt solution Selected from permanganate, sulfate, nitrate, chlorate or acetate.
5. a kind of preparation method of denitration demercuration monoblock type filtrate according to claim 1, characterized in that the original position is heavy Product agent is ammonium hydroxide, in sodium hydroxide, sodium carbonate, hexamethylenetetramine, urea, ammonium carbonate, ammonium chloride, ammonium fluoride, ammonium hydrogen carbonate It is one or more.
6. a kind of preparation method of denitration demercuration monoblock type filtrate according to claim 1, characterized in that in step (1) The disk for using impact style that diameter is made as 3cm in the metal fiber felt.
7. a kind of preparation method of denitration demercuration monoblock type filtrate according to claim 1, characterized in that in step (1) Supersound washing is carried out to the metal fiber felt using ethyl alcohol and hydrochloric acid.
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WO2020248723A1 (en) * 2019-05-31 2020-12-17 南京杰科丰环保技术装备研究院有限公司 Filter material integrating dust removal, denitration and mercury removal and preparation method therefor
CN112892551A (en) * 2021-01-28 2021-06-04 浙江工业大学 Composite porous filtering-catalyzing material and preparation method thereof
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CN113476958B (en) * 2021-06-22 2022-07-12 南京玻璃纤维研究设计院有限公司 Filter material and preparation method and application thereof
CN113813697A (en) * 2021-08-06 2021-12-21 中国科学院工程热物理研究所 Metal fiber filter material with dust removal and VOCs (volatile organic compounds) catalytic purification functions and preparation method thereof
CN114214076A (en) * 2021-12-13 2022-03-22 内蒙古万众炜业科技环保股份公司 Method for preparing full-particle-size briquette by coal cracking
CN114558587A (en) * 2022-03-17 2022-05-31 中南大学 Multi-metal composite cerium oxide material, preparation method thereof and application of multi-metal composite cerium oxide material as demercuration catalyst
CN114558587B (en) * 2022-03-17 2023-05-30 中南大学 Multi-metal composite cerium oxide material, preparation method thereof and application thereof as mercury removal catalyst

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