CN106925243A - A kind of microwave ultrasonic wave combines the methods and applications for preparing compound adsorbent - Google Patents

A kind of microwave ultrasonic wave combines the methods and applications for preparing compound adsorbent Download PDF

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Publication number
CN106925243A
CN106925243A CN201710195316.4A CN201710195316A CN106925243A CN 106925243 A CN106925243 A CN 106925243A CN 201710195316 A CN201710195316 A CN 201710195316A CN 106925243 A CN106925243 A CN 106925243A
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ultrasonic
mixed solution
ultrasonic wave
active carbon
water
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夏洪应
程松
张利波
彭金辉
舒建华
李春阳
蒋鑫
张奇
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Kunming University of Science and Technology
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    • 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
    • B01J20/20Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising free carbon; comprising carbon obtained by carbonising processes
    • 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
    • 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
    • B01J20/0203Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04
    • B01J20/0274Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04 characterised by the type of anion
    • B01J20/0296Nitrates of compounds other than those provided for in B01J20/04
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/283Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2220/00Aspects relating to sorbent materials
    • B01J2220/40Aspects relating to the composition of sorbent or filter aid materials
    • B01J2220/48Sorbents characterised by the starting material used for their preparation
    • B01J2220/4875Sorbents characterised by the starting material used for their preparation the starting material being a waste, residue or of undefined composition
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/12Halogens or halogen-containing compounds
    • C02F2101/14Fluorine or fluorine-containing compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/308Dyes; Colorants; Fluorescent agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/36Organic compounds containing halogen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/38Organic compounds containing nitrogen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/40Organic compounds containing sulfur

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Analytical Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

Combine the methods and applications for preparing compound adsorbent the present invention relates to a kind of microwave ultrasonic wave, belong to technical field of material.Waste active carbon is added to the water first be placed in ultrasonic environment and processed, pretreatment waste active carbon is dried to obtain after the completion for the treatment of;It is the mixed solution of 0.5mol/L that ferric nitrate and lanthanum nitrate are added sequentially to form concentration in the aqueous solution, mixed solution is placed in ultrasonic atomization generator, will pretreatment waste active carbon be placed in micro-wave oven, mist flow be 1~5ml/min, temperature be 600~900 DEG C under the conditions of be calcined 10~30min prepare Fe La compound adsorbents.The present invention with discarded activated carbon be raw material, in the microwave field using ultrasonic wave by the ferric nitrate of different mol ratio and lanthanum nitrate mixed solution with water smoke in the form of to discarding activated carbon loaded iron and lanthanum so as to obtain Fe La compound adsorbents.The method has accomplished to turn waste into wealth, and realizes recycling for discarded object, is conducive to alleviating the pressure of resource and environment, with superior economy and ecological benefits.

Description

A kind of microwave ultrasonic wave combines the methods and applications for preparing compound adsorbent
Technical field
Combine the methods and applications for preparing compound adsorbent the present invention relates to a kind of microwave ultrasonic wave, belong to material and prepare skill Art field.
Background technology
Activated carbon is widely used to because of its huge specific surface area, flourishing pore structure and extremely strong adsorption capacity The multiple fields such as chemical industry, pharmacy, environmental protection.With the development of human society, the consumption of activated carbon is increasing, and produced is useless Abandon activated carbon more and more, and if do not processed effectively using rear, severe contamination easily is caused to surrounding enviroment.Such as , using discarded activated carbon, presently mainly regenerating waste activated carbon recovers its absorption property, although this way is in certain journey for what Recycled discarded activated carbon on degree, but comparatively its surcharge is than relatively low.Therefore other are found suitable Method it is significant to improve the comprehensive utilization of resources efficiency of discarded activated carbon.
Waste water from dyestuff is the waste water that printworks is produced in economical production and discharges.According to relevant at present And public data, per one ton of processing, 100 200 tons of textile product water consumption, wherein will be turned into the 80% to 90% of water Waste water.The main feature of poisonous and hazardous waste water from dyestuff is water big, destructive strong, and alkalescence is big etc., in belonging to industrial wastewater Difficult type, the one of the main reasons as currently associated regional contaminated wastewater.Dyestuff in waste water can absorb light, drop Low water transparency, influences aquatile and growth of microorganism, is unfavorable for the self-purification of water, while easily causing visual pollution. The water body of severe contamination influences whether the health of the mankind.Therefore, the discharge to dyestuff must be controlled strictly, especially to those poison The serious dyestuff of evil, such as phthalocyanine bronze salt-dye and some azo dyes.
Fluorine is one of the essential trace elements of the human body, and the tooth and bone to human body are formed, Ca,P metabolism and internal enzyme System has important physiological action.But slow poisoning be can cause when fluorine excess intake, den tal fluorosis, severe patient even meeting caused Cause textured bone, pain, anchylosis, the calcification of muscle key, difficulty in walking, so that paralysis.In order to prevent and reducing fluorine disease hair Raw rate, the Oil repellent in control drinking water is very necessary.In the drinking water standard of the World Health Organization (WHO) suggestion, fluorine The concentration of compound is no more than 1.5mg/L.China exists《Standards for drinking water quality》(GB5949-2006) clear stipulaties in: Content of fluoride standard is not higher than 1.0mg/L in drinking water.
Therefore, find adsorption efficiency it is high, adsorption capacity is big, new adsorbent with low cost be used for waste water in dyestuff and Fluorine has turned into domestic and international important subject while having certain realistic meaning.
Applicant discloses a kind of " hydrothermal modification cotton boll inner casing suction in the patent of the A of Patent No. CN 102430394 The preparation method of attached defluorination material ", it is, with laminar cotton boll inner casing as raw material, to be entered using high-pressure hydrothermal reaction kettle to send elsewhere bright The thermally-denatured method of water-filling, obtains the cotton boll inner casing adsorption-defluorination material of bronzing flaky solid.Foregoing invention and the present invention Compare, two is that the invention is only adsorbed to fluorine, and maximal absorptive capacity is only 9.55mg/g.Two is the present invention not only having preferably to fluorine Adsorption effect, maximal absorptive capacity is 116.32mg/g, and also has preferable adsorption effect to dyestuff methylene blue.
Applicant discloses a kind of Acid Dye Wastewater inorganic agent in the patent of Patent No. 201410114987.X ", The raw material that the inorganic agent includes is:Aluminium polychloride, ferrous sulfate, active silicic acid, hydrogen peroxide, activated carbon, chlorine dioxide.In room The lower uniform stirring of temperature all dissolves each component, and 4 DEG C -60 DEG C of temperature in use is suitable to process sour water.The present invention will be by one Determine the Fenton reagent of ferrous sulfate and the hydrogen peroxide composition of weight, shape is combined with inorganic flocculating agent aluminium polychloride Into sewage-treating agent host, with active silicic acid as auxiliary agent, three's synergy, rapid subsidence suspension;Activated carbon and titanium dioxide Chloropexia, Quick disinfection, decolouring purify sewage.Foregoing invention is compared with the present invention:One is that the above method adds in preparation process Enter various auxiliary reagents, not only make that experimental implementation has become complicated but also so that whole process costs increased;Two is to use It is discarded activated carbon modified, turns waste into wealth, drastically increases the comprehensive utilization ratio and its surcharge of discarded object.
The content of the invention
For problem and deficiency that above-mentioned prior art is present, it is compound that the present invention provides a kind of microwave ultrasonic wave joint preparation The methods and applications of adsorbent.The present invention is raw material with discarded activated carbon, and ultrasonic wave is used in microwave field by different mol ratio Ferric nitrate and lanthanum nitrate mixed solution to discarded activated carbon loaded iron and lanthanum, so as to obtain, Fe-La is compound to be inhaled in the form of water smoke Attached dose.The method has accomplished to turn waste into wealth, and realizes recycling for discarded object, is conducive to alleviating the pressure of resource and environment, With superior economy and ecological benefits.The present invention is achieved through the following technical solutions.
A kind of microwave ultrasonic wave combines the method for preparing compound adsorbent, and it is comprised the following steps that:
(1)Waste active carbon is added to the water first be placed in ultrasonic environment and processed, pretreatment is dried to obtain after the completion for the treatment of useless Activated carbon;
(2)It is 1~5 according to mol ratio by ferric nitrate and lanthanum nitrate:1 is added sequentially to form concentration for 0.5mol/L in the aqueous solution Mixed solution, mixed solution is placed in ultrasonic atomization generator, will be through step(1)Obtain pretreatment waste active carbon be placed in it is micro- In ripple stove, mist flow be 1~5ml/min, temperature be 600~900 DEG C under the conditions of be calcined 10~30min prepare Fe- La compound adsorbents.
The step(1)Middle ultrasonic power is 50~150W.
A kind of Fe-La compound adsorbents are used to adsorb the fluorine in water.
The beneficial effects of the invention are as follows:
(1)This method production technology is very simple, and operation is comparatively simple, and energy consumption is relatively low, with low cost, and pollution-free;
(2)This method takes ultrasonic microwave to combine the mode for preparing compound adsorbent, not only make use of the cavitation of ultrasonic wave to make With the surface that ferric nitrate and lanthanum nitrate mixed solution are transported to super immixture waste active carbon in the form of ultrasonic atomization, So that ferric nitrate and lanthanum nitrate are more preferably supported on regenerated carbon;Outward microwave is also used to heat from the inside to surface and different material The characteristics of wave-absorbing effect is different, the water of ferric nitrate and lanthanum nitrate on rapid evaporation activated carbon allows ferric nitrate and lanthanum nitrate to contract rapidly Crystalline polyimide, fast decoupled forms loaded article in activated carbon surface;
(3)High efficiency composition adsorbent prepared by this method has up to 1158m2The specific surface area of/g, not only has to methylene blue Extraordinary adsorption effect, up to 293.71mg/g, but also has good adsorption effect to fluorine ion, up to 93mg/g.
(4)This method not only turns waste into wealth discarded activated carbon, realizes the comprehensive utilization of resources of the discarded object, reduces The discharge of discarded object, reduces environmental pollution, drastically increases the comprehensive utilization ratio and its surcharge of discarded object.
Brief description of the drawings
Fig. 1 is that the embodiment of the present invention 1 prepares Fe-La compound adsorbent scanning electron microscope (SEM) photographs;
Fig. 2 is that the embodiment of the present invention 1 prepares Fe-La compound adsorbent energy spectrum diagrams.
Specific embodiment
With reference to the accompanying drawings and detailed description, the invention will be further described.
Embodiment 1
The microwave ultrasonic wave combines the method for preparing compound adsorbent, and it is comprised the following steps that:
(1)Waste active carbon is added to the water first be placed in and 30min is processed in ultrasonic environment, pre- place is dried to obtain after the completion for the treatment of Reason waste active carbon;Wherein ultrasonic power is 150W;
(2)It is 4 according to mol ratio by ferric nitrate and lanthanum nitrate:1 to be added sequentially to form concentration in the aqueous solution be 0.5mol/L's Mixed solution, mixed solution is placed in ultrasonic atomization generator, will be through step(1)Obtain pretreatment waste active carbon and be placed in microwave In stove, mist flow be 3.5ml/min, temperature be 850 DEG C under the conditions of be calcined 20min prepare Fe-La compound adsorbents. Fe-La compound adsorbents scanning electron microscope (SEM) photograph is prepared as shown in figure 1, Fe-La compound adsorbent energy spectrum diagrams are as shown in Figure 2.
The methylene blue value of the Fe-La adsorbents prepared through above-mentioned steps is 293.71mg/g, the adsorption effect of fluorine ion Up to 93mg/g.
Embodiment 2
The microwave ultrasonic wave combines the method for preparing compound adsorbent, and it is comprised the following steps that:
(1)Waste active carbon is added to the water first be placed in and 30min is processed in ultrasonic environment, pre- place is dried to obtain after the completion for the treatment of Reason waste active carbon;Wherein ultrasonic power is 50W;
(2)It is 1 according to mol ratio by ferric nitrate and lanthanum nitrate:1 to be added sequentially to form concentration in the aqueous solution be 0.5mol/L's Mixed solution, mixed solution is placed in ultrasonic atomization generator, will be through step(1)Obtain pretreatment waste active carbon and be placed in microwave In stove, mist flow be 1ml/min, temperature be 600 DEG C under the conditions of be calcined 30min prepare Fe-La compound adsorbents;
The methylene blue value of the Fe-La adsorbents prepared through above-mentioned steps is 228.46mg/g, and the adsorption effect of fluorine ion is reachable 61 mg/g。
Embodiment 3
The microwave ultrasonic wave combines the method for preparing compound adsorbent, and it is comprised the following steps that:
(1)Waste active carbon is added to the water first be placed in and 30min is processed in ultrasonic environment, pre- place is dried to obtain after the completion for the treatment of Reason waste active carbon;Wherein ultrasonic power is 100W;
(2)It is 5 according to mol ratio by ferric nitrate and lanthanum nitrate:1 to be added sequentially to form concentration in the aqueous solution be 0.5mol/L's Mixed solution, mixed solution is placed in ultrasonic atomization generator, will be through step(1)Obtain pretreatment waste active carbon and be placed in microwave In stove, mist flow be 5ml/min, temperature be 900 DEG C under the conditions of be calcined 10min prepare Fe-La compound adsorbents.
The methylene blue value of the Fe-La adsorbents prepared through above-mentioned steps is 259.07mg/g, the adsorption effect of fluorine ion Up to 88mg/g.
Specific embodiment of the invention is explained in detail above in association with accompanying drawing, but the present invention be not limited to it is above-mentioned Implementation method, in the ken that those of ordinary skill in the art possess, can also be before present inventive concept not be departed from Put that various changes can be made.

Claims (3)

1. a kind of microwave ultrasonic wave combines the method for preparing compound adsorbent, it is characterised in that comprise the following steps that:
(1)Waste active carbon is added to the water first be placed in ultrasonic environment and processed, pretreatment is dried to obtain after the completion for the treatment of useless Activated carbon;
(2)It is 1~5 according to mol ratio by ferric nitrate and lanthanum nitrate:1 is added sequentially to form concentration for 0.5mol/L in the aqueous solution Mixed solution, mixed solution is placed in ultrasonic atomization generator, will be through step(1)Obtain pretreatment waste active carbon be placed in it is micro- In ripple stove, mist flow be 1~5ml/min, temperature be 600~900 DEG C under the conditions of be calcined 10~30min prepare Fe- La compound adsorbents.
2. microwave ultrasonic wave according to claim 1 combines the method for preparing compound adsorbent, it is characterised in that:The step Suddenly(1)Middle ultrasonic power is 50~150W.
3. a kind of Fe-La compound adsorbents according to claim 1 and 2 are used to adsorb the fluorine in water.
CN201710195316.4A 2017-03-29 2017-03-29 A kind of microwave ultrasonic wave combines the methods and applications for preparing compound adsorbent Pending CN106925243A (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108993382A (en) * 2018-06-25 2018-12-14 湖南烯富环保科技有限公司 A kind of defluorination material and its regeneration method based on bacteria residue
CN114797780A (en) * 2022-05-10 2022-07-29 太原理工大学 Device and method for preparing multi-metal-doped iron-based modified nano biological coke flue gas mercury adsorbent
CN116272864A (en) * 2023-02-24 2023-06-23 苏州西热节能环保技术有限公司 Adsorbent for removing mercury and sulfur trioxide in flue gas and preparation method thereof
CN117065766A (en) * 2023-10-16 2023-11-17 昆明理工大学 Preparation method of micron-sized sulfonic acid-based solid acid

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1431048A (en) * 2001-11-23 2003-07-23 中国科学院山西煤炭化学研究所 Load typed iron catalyst and its preparing method and application
CN103752268A (en) * 2014-01-16 2014-04-30 广东工业大学 Preparation method of filter core for adsorbing heavy metal, arsenic and fluorine in drinking water and application thereof
CN105251445A (en) * 2015-11-04 2016-01-20 中国科学院化学研究所 Porous carbon adsorbent as well as preparation method and application thereof

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1431048A (en) * 2001-11-23 2003-07-23 中国科学院山西煤炭化学研究所 Load typed iron catalyst and its preparing method and application
CN103752268A (en) * 2014-01-16 2014-04-30 广东工业大学 Preparation method of filter core for adsorbing heavy metal, arsenic and fluorine in drinking water and application thereof
CN105251445A (en) * 2015-11-04 2016-01-20 中国科学院化学研究所 Porous carbon adsorbent as well as preparation method and application thereof

Non-Patent Citations (5)

* Cited by examiner, † Cited by third party
Title
侯立安等: "《特殊废水处理技术及工程实例》", 31 October 2003, 化学工业出版社环境科学与工程出版中心 *
戴遐明等: "《纳米陶瓷材料及其应用》", 30 June 2005, 国防工业出版社 *
朱洪法等: "《催化剂制备及应用技术》", 30 June 2011, 中国石化出版社 *
褚睿智等: "微波技术在催化剂制备中的应用", 《现代化工》 *
赵梦华等: "铁-镧复合氧化物颗粒吸附剂除氟特性的研究", 《北京化工大学学报(自然科学版)》 *

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108993382A (en) * 2018-06-25 2018-12-14 湖南烯富环保科技有限公司 A kind of defluorination material and its regeneration method based on bacteria residue
CN108993382B (en) * 2018-06-25 2021-09-07 湖南烯富环保科技有限公司 Defluorination material based on mushroom dregs and regeneration method thereof
CN114797780A (en) * 2022-05-10 2022-07-29 太原理工大学 Device and method for preparing multi-metal-doped iron-based modified nano biological coke flue gas mercury adsorbent
CN114797780B (en) * 2022-05-10 2023-10-24 太原理工大学 Device and method for preparing multi-metal doped iron-based modified nano biological coke flue gas mercury adsorbent
CN116272864A (en) * 2023-02-24 2023-06-23 苏州西热节能环保技术有限公司 Adsorbent for removing mercury and sulfur trioxide in flue gas and preparation method thereof
CN117065766A (en) * 2023-10-16 2023-11-17 昆明理工大学 Preparation method of micron-sized sulfonic acid-based solid acid
CN117065766B (en) * 2023-10-16 2023-12-26 昆明理工大学 Preparation method of micron-sized sulfonic acid-based solid acid

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Application publication date: 20170707