CN112058219A - Preparation method and application of blast furnace ferronickel slag-based zeolite molecular sieve - Google Patents

Preparation method and application of blast furnace ferronickel slag-based zeolite molecular sieve Download PDF

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Publication number
CN112058219A
CN112058219A CN202010983637.2A CN202010983637A CN112058219A CN 112058219 A CN112058219 A CN 112058219A CN 202010983637 A CN202010983637 A CN 202010983637A CN 112058219 A CN112058219 A CN 112058219A
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blast furnace
molecular sieve
zeolite molecular
based zeolite
ferronickel slag
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雒云龙
周新涛
罗中秋
邵周军
刘钦
母维宏
韦宇
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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
    • B01J20/10Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
    • B01J20/16Alumino-silicates
    • B01J20/18Synthetic zeolitic molecular sieves
    • 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
    • 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
    • B01J2220/4887Residues, wastes, e.g. garbage, municipal or industrial sludges, compost, animal manure; fly-ashes
    • 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)
  • Inorganic Chemistry (AREA)
  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Analytical Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Water Treatment By Sorption (AREA)
  • Silicates, Zeolites, And Molecular Sieves (AREA)

Abstract

The invention discloses a preparation method of a blast furnace ferronickel slag-based zeolite molecular sieve, which comprises the steps of drying and grinding blast furnace ferronickel slag, adding sodium hydroxide, and roasting at 600-700 ℃ for 2 h; adding sodium hydroxide and deionized water into the roasted product, stirring for 30-60 min at room temperature, and aging overnight; transferring the mixture into a high-pressure reaction kettle, heating for 24 hours at 100-150 ℃, washing the product, performing suction filtration, drying and grinding to obtain the blast furnace ferronickel slag-based zeolite molecular sieve; the blast furnace ferronickel slag-based zeolite molecular sieve prepared by the invention is applied to adsorbing methylene blue, and experimental results show that the material has better adsorption performance on organic dye methylene blue.

Description

Preparation method and application of blast furnace ferronickel slag-based zeolite molecular sieve
Technical Field
The invention belongs to the technical field of organic dye wastewater treatment, and particularly relates to a preparation method of a blast furnace ferronickel slag-based zeolite molecular sieve and application of the zeolite molecular sieve in methylene blue adsorption.
Background
The methylene blue dye required by the textile industry is one of the most widely used water pollutants, which causes many health problems, such as abdominal disease, respiratory distress, skin allergies, and blindness. In addition, methylene blue dye adversely affects the environment and disrupts the balance of the ecosystem, which hinders photosynthesis by aquatic organisms, thus threatening the ecological environment.
Today, there are a variety of techniques for removing methylene blue dye, such as ultrafiltration, ozonation, reverse osmosis, ion exchange, chemical oxidation, photodegradation, solvent extraction, electrochemical degradation, and adsorption. Wherein the adsorption method is simple, easy, effective and economical. The commonly used adsorbent comprises zeolite, activated carbon, multi-wall carbon nano-tubes and polymers, and the electromotive potential of the zeolite is negative, so that the adsorbent has a good adsorption effect on the cationic dye methylene blue.
The blast furnace ferronickel slag is metal slag generated in blast furnace production operation and contains rich SiO2And Al2O3The zeolite molecular sieve prepared by the method not only provides an efficient adsorbent preparation method, but also solves the problem that a large amount of blast furnace ferronickel slag is stacked to occupy land resources, and provides a new idea for resource utilization of the blast furnace ferronickel slag.
Disclosure of Invention
The invention provides a preparation method of a blast furnace ferronickel slag-based zeolite molecular sieve, which not only solves the pollution of methyl blue in wastewater, but also solves the problem that a large amount of blast furnace ferronickel slag is stacked to occupy land resources, and the method comprises the following steps:
(1) drying and grinding the blast furnace ferronickel slag, adding sodium hydroxide, and roasting at 600-700 ℃ for 2 h; the mass ratio of the blast furnace nickel-iron slag to the sodium hydroxide is 1: 1.5-2;
(2) adding sodium hydroxide and deionized water into the roasted product obtained in the step (1), stirring at room temperature for 30-60 min, aging overnight, wherein the mass ratio of the roasted product to the sodium hydroxide is 1-3: 1, and the mass volume ratio g: mL of the roasted product to the deionized water is 1: 15-20;
(3) and (3) transferring the mixture obtained in the step (2) into a high-pressure reaction kettle, heating for 24 hours at 100-150 ℃, washing the product, performing suction filtration, drying and grinding to obtain the blast furnace ferronickel slag-based zeolite molecular sieve.
The blast furnace ferronickel slag mainly comprises the following components: SiO 2226~31wt%、Al2O319-35 wt%, 10-14 wt% of MgO, and 19-30 wt% of CaO; the blast furnace ferronickel slag is waste slag powder which is ground and then sieved by a 80-mesh sieve, and the balance of the sieve is less than 5%.
The invention also aims to apply the blast furnace ferronickel slag-based zeolite molecular sieve prepared by the method to a methylene blue adsorbent.
The technical scheme of the invention has the advantages and the technical effects that:
the invention adopts blast furnace nickel-iron slag as a main raw material, is matched with sodium hydroxide, adopts a hydrothermal method to prepare the zeolite molecular sieve, and uses the material to adsorb methylene blue; the material has a remarkable effect of adsorbing methylene blue, can effectively recycle industrial waste residues, improves the comprehensive utilization rate of blast furnace nickel-iron slag, and provides a new idea for treating methylene blue polluted water.
Detailed Description
In order to better understand the contents of the present invention, the present invention will be further described in detail by the following specific examples, but the scope of the present invention is not limited to the contents, and the blast furnace ferronickel slag used in the examples mainly comprises the following components: SiO 2226~31wt%、Al2O319~35wt%、MgO10~14wt%、CaO19~30wt%
Example 1: preparation method of blast furnace nickel-iron slag based zeolite molecular sieve
And (2) uniformly mixing 58.8g of dry blast furnace ferronickel slag (which is ground and sieved by a 80-mesh sieve, and the sieve residue is less than 5%) with 100g of sodium hydroxide, placing the mixture into a muffle furnace to be roasted for 2h at 650 ℃, weighing 10g of roasted solid and 5g of sodium hydroxide to be mixed, adding 200mL of deionized water, stirring for 1h at room temperature, aging and staying overnight, transferring the mixture into a high-pressure reaction kettle, heating for 24h at 100 ℃, washing, filtering, drying and grinding the mixture to obtain the blast furnace ferronickel slag-based zeolite molecular sieve.
Example 2: preparation method of blast furnace nickel-iron slag-based zeolite molecular sieve
Uniformly mixing dry blast furnace nickel-iron slag (which is ground and sieved by a 80-mesh sieve, and the balance of the sieve is less than 5%) with sodium hydroxide, wherein the mass ratio of the blast furnace nickel-iron slag to the sodium hydroxide is 1:2, placing the blast furnace nickel-iron slag and the sodium hydroxide into a muffle furnace to roast for 2 hours at 700 ℃, weighing roasted solid, mixing the solid with the sodium hydroxide, and adding deionized water, wherein the mass ratio of the roasted product to the sodium hydroxide is 1:1, and the mass-volume ratio g: mL of the roasted product to the deionized water is 1: 15; stirring for 1h at room temperature, aging and standing overnight, transferring the mixture into a high-pressure reaction kettle, heating for 24h at 120 ℃, washing, filtering, drying and grinding the mixture to obtain the blast furnace ferronickel slag-based zeolite molecular sieve.
Example 3: preparation method of blast furnace nickel-iron slag-based zeolite molecular sieve
Uniformly mixing dry blast furnace nickel-iron slag (which is ground and sieved by a 80-mesh sieve, and the balance of the sieve is less than 5%) with sodium hydroxide, wherein the mass ratio of the blast furnace nickel-iron slag to the sodium hydroxide is 1:1.5, placing the blast furnace nickel-iron slag and the sodium hydroxide into a muffle furnace to roast for 2 hours at 600 ℃, weighing roasted solid, mixing the solid with the sodium hydroxide, and adding deionized water, wherein the mass ratio of the roasted product to the sodium hydroxide is 3:1, and the mass-volume ratio g: mL of the roasted product to the deionized water is 1: 18; stirring for 1h at room temperature, aging and standing overnight, transferring the mixture into a high-pressure reaction kettle, heating for 24h at 150 ℃, washing, filtering, drying and grinding the mixture to obtain the blast furnace ferronickel slag-based zeolite molecular sieve.
The blast furnace ferronickel slag-based zeolite molecular sieve prepared by the embodiment is used for methylene blue, and the influence of the concentration of the methylene blue on the adsorption effect is detected
The initial concentration of the liquid containing methylene blue to be treated is respectively 200mg/L, 250mg/L, 300mg/L, 350mg/L, 400mg/L and 1000mg/L, each concentration is 30mL, then 0.1g of blast furnace ferronickel slag-based zeolite molecular sieve is added into each detection sample, stirring treatment is carried out in a horizontal constant temperature oscillator, the parameters of the horizontal constant temperature oscillator are set to be 25 ℃ and 120r/min, standing is carried out for 30min after oscillation is carried out for 240min, supernatant liquid is taken, the content of the methylene blue in the solution is measured, and the adsorption rate and the adsorption capacity of the blast furnace ferronickel slag-based zeolite molecular sieve to the methylene blue in the solution are calculated, and the results are shown in Table 1; as can be seen from Table 1, the effect of the blast furnace nickel-iron slag-based zeolite molecular sieve on adsorbing methylene blue in the solution is different under different initial concentration conditions; along with the increase of the initial concentration, the effect of the blast furnace ferronickel slag-based zeolite molecular sieve on adsorbing methylene blue in the solution is in a decreasing trend, and when the initial concentration reaches 1000mg/L, the adsorption rate and the adsorption capacity are still higher, which shows that the blast furnace ferronickel slag-based zeolite molecular sieve has a good adsorption effect on methylene blue wastewater solution.
TABLE 1 adsorption rate and adsorption capacity of blast furnace ferronickel slag-based zeolite molecular sieve for methylene blue of different concentrations
Figure DEST_PATH_IMAGE001
Influence of different pH values on adsorption of methylene blue by blast furnace nickel-iron slag-based zeolite molecular sieve
Adjusting initial pH values of the solution to be treated to be 2, 3, 4, 5, 6, 7, 8, 9 and 10 by using 1mol/L hydrochloric acid solution and 1mol/L sodium hydroxide solution, respectively, adjusting the initial pH values to be 2, 3, 4, 5, 6, 7, 8, 9 and 10, respectively adding 0.1g of blast furnace ferronickel slag-based zeolite molecular sieve, setting parameters of a horizontal constant temperature oscillator to be 25 ℃ and 120r/min, standing for 30min after oscillation for 240min, absorbing supernatant by using an injector, measuring the content of methylene blue in the solution, and calculating the adsorption rate and the adsorption capacity of the blast furnace slag-based zeolite molecular sieve to the methylene blue in the ferronickel solution, wherein the results are shown in Table 2; as can be seen from Table 2, the effect of adsorbing methylene blue in the solution by the blast furnace nickel-iron slag-based zeolite molecular sieve is different under different pH conditions; along with the increase of the pH value, the effect of the blast furnace nickel-iron slag-based zeolite molecular sieve on adsorbing methylene blue in the solution is increased; when the pH value is 6, the adsorption rate of the methylene blue in the blast furnace ferronickel slag-based zeolite molecular sieve adsorption solution can reach 87.5 percent, and the change of the adsorption rate and the adsorption capacity is not large afterwards.
TABLE 2 effect of adsorption of methylene blue in blast furnace ferronickel slag-based zeolite molecular sieves under different pH conditions
Figure 386212DEST_PATH_IMAGE002
Influence of different adsorption temperatures on adsorption of methylene blue by blast furnace ferronickel slag-based zeolite molecular sieve
Adding 0.1g of blast furnace ferronickel slag-based zeolite molecular sieve into a liquid to be treated, setting the temperature of a horizontal constant-temperature oscillator to be 25 ℃, 35 ℃ and 45 ℃, oscillating for 240min at 120r/min, standing for 30min, absorbing supernatant by using an injector, determining the content of methylene blue in the solution, and calculating the adsorption rate and the adsorption capacity of the blast furnace ferronickel slag-based zeolite molecular sieve on the methylene blue in the solution; the results are shown in Table 3; as can be seen from table 3, the adsorption amount and removal rate of methylene blue were reduced at elevated temperatures, and therefore, when methylene blue was adsorbed by the blast furnace nickel-iron slag-based zeolite molecular sieve, a good adsorption effect was obtained at room temperature, and it was not necessary to raise the temperature and reduce the energy consumption.
TABLE 3 effect of adsorption of methylene blue in blast furnace ferronickel slag-based zeolite molecular sieves at different adsorption temperatures
Figure DEST_PATH_IMAGE003
In conclusion, when the blast furnace ferronickel slag-based zeolite molecular sieve adsorbs heavy methylene blue in the solution, the adsorption pH is recommended to be 6 respectively, and the adsorption temperature is recommended to be 25 ℃ respectively, so that the adsorption rate and the adsorption capacity of the methylene blue can be maximized.
In the above embodiment, when the furnace ferronickel slag-based zeolite molecular sieve adsorbs methylene blue in the solution, the adsorption rate R and the adsorption capacity Q are calculated by the following formulas:
Figure DEST_PATH_IMAGE005
Q=(Ct-C0)×V/m
in the formula: c0And CtRespectively representing the initial concentration of the methylene blue solution and the residual concentration of the methylene blue solution at the t moment, wherein mg/L, V is the volume of the adsorption amount, and m is the dosage of the adsorbent.
It should be emphasized that the above-described embodiments are merely examples for clearly illustrating the present invention and are not to be considered as a complete limitation of the embodiments. Other variants will be apparent to those skilled in the art on the basis of the foregoing description, and it is not necessary to exemplify all the embodiments herein, but rather obvious variations are contemplated which are within the scope of the invention.

Claims (6)

1. A preparation method of a blast furnace ferronickel slag-based zeolite molecular sieve is characterized by comprising the following steps:
(1) drying and grinding the blast furnace ferronickel slag, adding sodium hydroxide, and roasting at 600-700 ℃ for 2 h;
(2) adding sodium hydroxide and deionized water into the roasted product in the step (1), stirring for 30-60 min at room temperature, and aging overnight;
(3) and (3) transferring the mixture obtained in the step (2) into a high-pressure reaction kettle, heating for 24 hours at 100-150 ℃, washing the product, performing suction filtration, drying and grinding to obtain the blast furnace ferronickel slag-based zeolite molecular sieve.
2. The preparation method of the blast furnace ferronickel slag-based zeolite molecular sieve according to claim 1, characterized in that: the mass ratio of the blast furnace nickel-iron slag to the sodium hydroxide is 1: 1.5-2.
3. The preparation method of the blast furnace ferronickel slag-based zeolite molecular sieve according to claim 1, characterized in that: the mass ratio of the roasted product to the sodium hydroxide is 1-3: 1.
4. The preparation method of the blast furnace ferronickel slag-based zeolite molecular sieve according to claim 1, characterized in that: the blast furnace ferronickel slag is waste slag powder which is ground and then sieved by a 80-mesh sieve, and the balance of the sieve is less than 5%.
5. The preparation method of the blast furnace ferronickel slag-based zeolite molecular sieve according to claim 1, characterized in that: the mass volume ratio g: mL of the roasted product to the deionized water is 1: 15-20.
6. The use of the blast furnace nickel iron slag-based zeolite molecular sieve prepared by the method for preparing the blast furnace nickel iron slag-based zeolite molecular sieve according to any one of claims 1 to 5 in the adsorption of methylene blue.
CN202010983637.2A 2020-09-17 2020-09-17 Preparation method and application of blast furnace ferronickel slag-based zeolite molecular sieve Pending CN112058219A (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113231007A (en) * 2021-06-07 2021-08-10 北京科技大学 Method for preparing heavy metal adsorbent by using blast furnace slag and application
CN113461026A (en) * 2021-07-09 2021-10-01 盐城工学院 Preparation method and application of zeolite type phosphorus removal agent for high-salt waste liquid

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CN105036150A (en) * 2015-06-26 2015-11-11 中国矿业大学(北京) Artificial zeolite prepared directionally by utilizing industrial solid waste and preparation method and application thereof
CN106544457A (en) * 2016-11-08 2017-03-29 重庆大学 Based on the CO that blast furnace slag waste heat recovery and slag charge are utilized2Emission-reducing system and method
JP2018158878A (en) * 2017-03-22 2018-10-11 裕史 笠松 Zeolite-containing composition and method for producing zeolite-containing composition
CN109248648A (en) * 2018-10-25 2019-01-22 福州大学 A kind of modified bauxite for adsorption treatment heavy metal ions in wastewater
CN109589915A (en) * 2018-11-09 2019-04-09 广州润方环保科技有限公司 A kind of method and its application using iron and steel pickling waste liquid and the magnetic bio charcoal of agriculture and forestry organic waste material preparation removal Cr VI

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CN103752265A (en) * 2014-01-13 2014-04-30 福建工程学院 Preparation method and application of composite modified zeolite
CN105036150A (en) * 2015-06-26 2015-11-11 中国矿业大学(北京) Artificial zeolite prepared directionally by utilizing industrial solid waste and preparation method and application thereof
CN106544457A (en) * 2016-11-08 2017-03-29 重庆大学 Based on the CO that blast furnace slag waste heat recovery and slag charge are utilized2Emission-reducing system and method
JP2018158878A (en) * 2017-03-22 2018-10-11 裕史 笠松 Zeolite-containing composition and method for producing zeolite-containing composition
CN109248648A (en) * 2018-10-25 2019-01-22 福州大学 A kind of modified bauxite for adsorption treatment heavy metal ions in wastewater
CN109589915A (en) * 2018-11-09 2019-04-09 广州润方环保科技有限公司 A kind of method and its application using iron and steel pickling waste liquid and the magnetic bio charcoal of agriculture and forestry organic waste material preparation removal Cr VI

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113231007A (en) * 2021-06-07 2021-08-10 北京科技大学 Method for preparing heavy metal adsorbent by using blast furnace slag and application
CN113461026A (en) * 2021-07-09 2021-10-01 盐城工学院 Preparation method and application of zeolite type phosphorus removal agent for high-salt waste liquid
CN113461026B (en) * 2021-07-09 2023-11-10 盐城工学院 Preparation method and application of zeolite type dephosphorizing agent for high-salt waste liquid

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Application publication date: 20201211