CN115254000A - Synthetic method and application of magnetic coal gasification slag-based magnesium adsorbent - Google Patents

Synthetic method and application of magnetic coal gasification slag-based magnesium adsorbent Download PDF

Info

Publication number
CN115254000A
CN115254000A CN202210944379.6A CN202210944379A CN115254000A CN 115254000 A CN115254000 A CN 115254000A CN 202210944379 A CN202210944379 A CN 202210944379A CN 115254000 A CN115254000 A CN 115254000A
Authority
CN
China
Prior art keywords
magnesium
adsorbent
magnetic
coal gasification
slag
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.)
Granted
Application number
CN202210944379.6A
Other languages
Chinese (zh)
Other versions
CN115254000B (en
Inventor
姚志通
孙宇航
陈昕洋
王彬惠
刘洁
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.)
Hangzhou Dianzi University
Original Assignee
Hangzhou Dianzi University
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 Hangzhou Dianzi University filed Critical Hangzhou Dianzi University
Priority to CN202210944379.6A priority Critical patent/CN115254000B/en
Publication of CN115254000A publication Critical patent/CN115254000A/en
Application granted granted Critical
Publication of CN115254000B publication Critical patent/CN115254000B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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
    • B01J20/06Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
    • 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
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28002Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their physical properties
    • B01J20/28009Magnetic properties
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01DCOMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
    • C01D15/00Lithium compounds
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B26/00Obtaining alkali, alkaline earth metals or magnesium
    • C22B26/10Obtaining alkali metals
    • C22B26/12Obtaining lithium
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B26/00Obtaining alkali, alkaline earth metals or magnesium
    • C22B26/20Obtaining alkaline earth metals or magnesium
    • C22B26/22Obtaining magnesium
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B3/00Extraction of metal compounds from ores or concentrates by wet processes
    • C22B3/20Treatment or purification of solutions, e.g. obtained by leaching
    • C22B3/22Treatment or purification of solutions, e.g. obtained by leaching by physical processes, e.g. by filtration, by magnetic means, or by thermal decomposition
    • C22B3/24Treatment or purification of solutions, e.g. obtained by leaching by physical processes, e.g. by filtration, by magnetic means, or by thermal decomposition by adsorption on solid substances, e.g. by extraction with solid resins
    • 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
    • B01J2220/4806Sorbents characterised by the starting material used for their preparation the starting material being of inorganic character
    • 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
    • B01J2220/4812Sorbents characterised by the starting material used for their preparation the starting material being of organic character
    • 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
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Abstract

The invention discloses a method for synthesizing a magnetic coal gasification slag-based magnesium adsorbent. Mixing the coal gasification coarse slag and an electrolyte solution, putting the mixture into a plasma ball mill, and carrying out ball milling for 3-5h at an excitation voltage of 3-10kV and a rotating speed of 400-800 r/min. The product is transferred and heated to 200-500 ℃ and reacts for 1-3h under the steam atmosphere. Soaking the product in magnesium alginate and amino acidsIn the iron solution, centrifuging after ultrasonic oscillation for 1-3h. Transferring the solid product into a tubular reaction furnace, heating to 300-600 ℃, and reacting for 1-5h under the steam atmosphere. Soaking the product in dilute acid solution, reacting for 0.5-2 hr, centrifuging, and drying to obtain product with specific surface area of 300-500m 2 The adsorbent has a pore diameter of 2-70nm and a magnesium adsorption capacity of 30-60mg/g. The method takes the coal gasification coarse slag as a raw material, and obtains the magnetic multilevel pore magnesium adsorbent by the reinforced load of the plasma ball mill, the micro-etching modification of electrolyte and the magnesium dipping modification, and the magnetic multilevel pore magnesium adsorbent can be used for extracting and separating magnesium in salt lake brine, and reduces the magnesium-lithium ratio, and has the advantages of simple preparation process, high magnesium ion selectivity, large adsorption capacity and the like.

Description

Synthetic method and application of magnetic coal gasification slag-based magnesium adsorbent
Technical Field
The invention belongs to the technical field of adsorbent preparation, and particularly relates to a synthetic method of a magnetic coal gasification slag-based magnesium adsorbent.
Background
Magnesium, lithium and compounds thereof have important strategic positions in national economy and national defense construction. In the middle of the 80 th century in the last century, lithium salts were produced mainly from lithium ores in countries of the world. The method has long history and mature process, but has high energy consumption, can pollute the environment to a certain extent, and increasingly lacks the lithium ore resources, thereby increasingly showing the limitation. On the other hand, the lithium storage capacity of the salt lake brine is rich, the cost is lower than that of the exploitation of lithium ores, and the lithium extraction from the salt lake gradually becomes a development trend along with the exploration and development of lithium resources in the huge salt lake brine in south America. China is a large lithium resource country, and reserves are in the forefront of the world. Wherein, the lithium resource reserves of the salt lake of Qinghai and Tibet account for more than 85 percent of the total reserves. Generally, the ratio of magnesium to lithium in the brine of the salt lake determines the feasibility of producing lithium salt by using brine resources and the production cost and economic benefit of lithium salt products. However, the Qinghai salt lake brine has high magnesium-lithium ratio which is dozens to hundreds or even thousands, the magnesium-lithium ratio in the east Gillel salt lake old brine with relatively small magnesium-lithium ratio also reaches 20: 1, and the problems of high difficulty in lithium extraction, high production cost and the like are caused by the excessively high magnesium-lithium ratio.
The prior method for separating magnesium and lithium from salt lake brine comprises a precipitation method, a calcination leaching method, an extraction method, a membrane separation method, an adsorption method and the like. The precipitation method is simple in process and low in cost, and is suitable for extracting lithium from the salt lake brine with low magnesium-lithium ratio. However, when the magnesium and lithium are relatively large, the method causes excessive alkali consumption and serious lithium salt loss. The adsorption method has the advantages of simple process, high recovery rate, environmental friendliness and the like, and the magnesium-lithium ratio can be reduced by selectively adsorbing magnesium. However, the research and development on magnesium adsorbents are relatively few. Therefore, the development of the adsorbent with high magnesium ion selectivity and large adsorption capacity has great significance for reducing the magnesium-lithium ratio and comprehensively utilizing magnesium-lithium resources.
Disclosure of Invention
The invention aims to overcome the defects of the prior art and provides a synthetic method of a magnetic coal gasification slag-based magnesium adsorbent;
the method comprises the following steps:
step (1), mixing the coal gasification coarse slag and an electrolyte solution containing magnesium ions according to a solid-to-liquid ratio of 1:5-10 (g/ml) of the raw materials are mixed and then placed in a plasma ball mill, and the mixture is ball milled for 3-5 hours under the excitation voltage of 3-10kV and the rotating speed of 400-800 r/min;
transferring the product after ball milling treatment to a tubular reaction furnace, heating to 200-500 ℃, and reacting for 1-3h in a water vapor atmosphere;
and (3) enabling a reaction product obtained in the tubular furnace in the step (2) to react according to a solid-to-liquid ratio of 1:10-20 (g/ml) of the solid product is immersed in a magnesium alginate and ferric amino acid solution, and the solid product is obtained by centrifugal separation after ultrasonic oscillation for 1-3h.
And (4) transferring the solid product to a tubular reaction furnace, heating to 300-600 ℃, and reacting for 1-5h in a water vapor atmosphere.
And (5) mixing the reaction product obtained in the step (4) according to a solid-liquid ratio of 1:5 to 10 g/ml of the magnetic coal gasification slag-based magnesium adsorbent is soaked in 0.5 to 2mol/L of dilute acid solution, centrifugally separated after reacting for 0.5 to 2 hours, and dried to obtain the magnetic coal gasification slag-based magnesium adsorbent.
Preferably, in the step (1), the electrolyte is one or more of magnesium hexafluorophosphate, magnesium perchlorate, magnesium tetrafluoroborate, magnesium hexafluoroarsenate, magnesium bistrifluoromethanesulfonylimide, perfluoroalkyl sulfonyl methyl magnesium and magnesium difluoro oxalate borate; the molar concentration of the electrolyte is 0.2-2mol/L.
Preferably, in step (3), the solution is prepared in the following manner: the molar concentration of magnesium alginate is 3-5mol/L, the molar concentration of ferric amino acid is 2-6mol/L, and the volume ratio of the mixture of the magnesium alginate and the ferric amino acid is 1:0.2-0.6.
Preferably, in the step (5), the diluted acid is one or more of hydrochloric acid, sulfuric acid and nitric acid.
Preferably, the magnetic coal gasification slag-based magnesium adsorbent obtained in the step (5)Has a specific surface area of 300-500m 2 The pore diameter is 2-70nm, and the magnesium adsorption capacity is 30-60mg/g.
The invention also provides the magnetic coal gasification slag-based magnesium adsorbent prepared by the synthesis method of the magnetic coal gasification slag-based magnesium adsorbent.
The invention also provides a method for extracting lithium from salt lake brine by using the magnetic coal gasification slag-based magnesium adsorbent, which comprises the following steps:
s1, extracting magnesium in salt lake brine by using the magnetic coal gasification slag-based magnesium adsorbent to reduce the magnesium-lithium ratio;
s2, extracting lithium from the salt lake brine with the magnesium-lithium ratio reduced.
The method takes the coal gasification coarse slag as a raw material, the coal gasification coarse slag is subjected to reinforced loading of magnesium through a plasma ball mill and an electrolyte solution, and then the coal gasification coarse slag is activated in a steam atmosphere of a tubular reaction furnace, wherein the electrolyte is decomposed to carry out micro-etching on the coal gasification coarse slag, so that the specific surface area of the coal gasification coarse slag is increased, and the pore structure is improved. The selectivity of magnesium ions is improved by acid elution after the magnesium alginate is impregnated. The purpose of magnetic separation is achieved by loading ferric amino acid and performing heat treatment to make the magnetic iron magnetic. Therefore, the invention overcomes the defects of small adsorption capacity, low selectivity and difficult separation of the traditional magnesium adsorbent, has the advantages of simple preparation process, high magnesium ion selectivity, large adsorption capacity, easy separation and the like, and is easy for large-scale production and application.
Detailed Description
In order to make the objects, technical solutions and advantages of the present application more apparent, the present application is further described in detail with reference to the following embodiments. It should be understood that the specific embodiments described herein are merely illustrative of and not restrictive on the broad application.
Example 1:
1. a synthetic method of a magnetic coal gasification slag-based magnesium adsorbent is characterized by comprising the following steps:
(1) And mixing the coal gasification coarse slag with 0.2mol/L magnesium hexafluorophosphate solution according to the solid-to-liquid ratio of 1:5 mixing, placing in a plasma ball mill, and carrying out ball milling for 3 hours at an excitation voltage of 3kV and a rotation speed of 400 r/min;
(2) Transferring the product after ball milling treatment to a tubular reaction furnace, heating to 200 ℃, and reacting for 1h in a water vapor atmosphere;
(3) And mixing the reaction product in the tubular furnace according to the solid-liquid ratio of 1:10, soaking in 3mol/L magnesium alginate and 2mol/L ferric amino acid solution, wherein the volume ratio of the two is 1: and (3) 0.2, carrying out ultrasonic oscillation for 1h, and then carrying out centrifugal separation to obtain a solid product.
(4) And transferring the solid product into a tubular reaction furnace, heating to 300 ℃, and reacting for 1h in a water vapor atmosphere.
(5) And reacting products in a solid-liquid ratio of 1:5 is soaked in 0.5mol/L hydrochloric acid solution, centrifugal separation is carried out after 0.5h of reaction, and the specific surface area is 300m after drying 2 The adsorbent has a pore diameter of 2-30nm and a magnesium adsorption capacity of 30 mg/g.
Example 2:
(1) And mixing the coal gasification coarse slag and 2mol/L magnesium perchlorate solution according to the solid-liquid ratio of 1:10, mixing, placing in a plasma ball mill, and carrying out ball milling for 5 hours at an excitation voltage of 10kV and a rotation speed of 800 r/min;
(2) Transferring the product after ball milling treatment to a tubular reaction furnace, heating to 500 ℃, and reacting for 3 hours in a water vapor atmosphere;
(3) And mixing the reaction product in the tubular furnace according to the solid-liquid ratio of 1:20, soaking in 5mol/L magnesium alginate and 6mol/L ferric amino acid solution, wherein the volume ratio of the two is 1:0.6, carrying out ultrasonic oscillation for 3 hours, and then carrying out centrifugal separation to obtain a solid product.
(4) And transferring the solid product into a tubular reaction furnace, heating to 600 ℃, and reacting for 5 hours in a water vapor atmosphere.
(5) And (3) mixing the products after the reaction according to a solid-liquid ratio of 1:10 is immersed in 2mol/L sulfuric acid solution, centrifugal separation is carried out after 2h reaction, and the specific surface area is 500m after drying 2 The adsorbent has a pore diameter of 5-70nm and a magnesium adsorption capacity of 60mg/g.
Example 3:
(1) And mixing the coal gasification coarse slag with 0.5mol/L magnesium tetrafluoroborate solution according to the solid-to-liquid ratio of 1:6 mixing, placing in a plasma ball mill, and ball-milling for 4 hours at an excitation voltage of 5kV and a rotation speed of 600 r/min;
(2) Transferring the product after ball milling treatment to a tubular reaction furnace, heating to 300 ℃, and reacting for 1.5h in a water vapor atmosphere;
(3) And (3) mixing the reaction product in the tubular furnace according to the solid-liquid ratio of 1:15, soaking in 3.5mol/L magnesium alginate and 4mol/L ferric amino acid solution, wherein the volume ratio of the two is 1: and (3) carrying out ultrasonic oscillation for 1.5h, and then carrying out centrifugal separation to obtain a solid product.
(4) And transferring the solid product to a tubular reaction furnace, heating to 400 ℃, and reacting for 3 hours in a water vapor atmosphere.
(5) And (3) mixing the products after the reaction according to a solid-liquid ratio of 1:6 is immersed in 1.5mol/L nitric acid solution, centrifugal separation is carried out after 1 hour of reaction, and the specific surface area is 350m after drying 2 The adsorbent has a pore diameter of 10-50nm and a magnesium adsorption capacity of 45 mg/g.
Example 4:
(1) And mixing the coal gasification coarse slag with 0.8mol/L bis (trifluoromethanesulfonimide) magnesium solution according to a solid-to-liquid ratio of 1:7.5 mixing, placing in a plasma ball mill, and ball milling for 3h at an excitation voltage of 7.5kV and a rotation speed of 650 r/min;
(2) Transferring the product after ball milling treatment to a tubular reaction furnace, heating to 350 ℃, and reacting for 3 hours in a water vapor atmosphere;
(3) And mixing the reaction product in the tubular furnace according to the solid-liquid ratio of 1:13, soaking in 3mol/L magnesium alginate and 5.5mol/L ferric amino acid solution, wherein the volume ratio of the two is 1: and (3) carrying out ultrasonic oscillation for 2.5 hours, and then carrying out centrifugal separation to obtain a solid product.
(4) And transferring the solid product to a tubular reaction furnace, heating to 400 ℃, and reacting for 3 hours in a water vapor atmosphere.
(5) And (3) mixing the products after the reaction according to a solid-liquid ratio of 1:7 is immersed in 0.5mol/L dilute hydrochloric acid and sulfuric acid solution (volume ratio 1 2 The/g, the aperture is 5-60nm, and the magnesium adsorption capacity is 55 mg/g.
Example 5:
(1) Mixing the coal gasification coarse slag with 0.4mol/L perfluoroalkyl sulfonyl methyl magnesium and 1mol/L difluoro oxalic acid magnesium borate solution (volume ratio 1:6, mixing, placing in a plasma ball mill, and carrying out ball milling for 5 hours at an excitation voltage of 4kV and a rotation speed of 700 r/min;
(2) Transferring the product after ball milling treatment to a tubular reaction furnace, heating to 400 ℃, and reacting for 2 hours in a water vapor atmosphere;
(3) And mixing the reaction product in the tubular furnace according to the solid-liquid ratio of 1:10, soaking the mixture in 4mol/L magnesium alginate and 2mol/L ferric amino acid solution, wherein the volume ratio of the two is 1:0.45, carrying out ultrasonic oscillation for 2 hours, and then carrying out centrifugal separation to obtain a solid product.
(4) And transferring the solid product into a tubular reaction furnace, heating to 550 ℃, and reacting for 4.5h under a water vapor atmosphere.
(5) And (3) mixing the products after the reaction according to a solid-liquid ratio of 1:8, soaking in 0.8mol/L dilute hydrochloric acid and nitric acid solution (volume ratio is 1 2 The adsorbent has a pore diameter of 8-60nm and a magnesium adsorption capacity of 48 mg/g.
Specific surface area and pore size distribution were tested in a nitrogen atmosphere using a Micromeritics ASAP 2020 analyzer.
Testing of magnesium ion adsorption capacity: and (3) mixing the adsorbent according to a solid-liquid ratio of 1:20 adding the mixture into simulated brine, adsorbing the mixture for a certain time in a constant-temperature water bath, centrifuging the mixture to obtain supernatant, and detecting the concentration of magnesium ions in the brine by using an inductively coupled plasma emission spectrometer. Adsorption capacity Qt as Qt = (rho) 01 ) V/m is calculated, wherein Qt is the adsorption capacity at the t moment, mg/g; ρ is a unit of a gradient 0 The mass concentration of initial magnesium ions of the solution is mg/L; ρ is a unit of a gradient 1 The mass concentration of the magnesium ions after adsorption is mg/L, m is the mass of the adsorbent, g; v is the volume of the adsorption solution, L. Compared with the prior art, the invention has the advantages of simple preparation process, high magnesium ion selectivity, large adsorption capacity and the like.
The adsorption performance of kaolinite, coal and montmorillonite on magnesium ions is researched by the research on the adsorption characteristics of calcium and magnesium ions in coal slurry water [ J ]. Chinese coal, 2011,37 (11): 71-74 ], and the saturated adsorption capacity distribution of the three adsorbents is 5mg/g, 1mg/g and 0.5mg/g. The adsorption characteristics of the modified sawdust on calcium and magnesium ions are researched by He Yu Yan [ He Yu Yan & gt ] energy and environment, 2009 (02): 17-18+47 ], so that the saturated adsorption capacity of the magnesium ions is investigated, and the saturated adsorption capacity is 24.13mg/g under a static condition. Li Jian [ Li Jian. Kaolin preparation white carbon black and experimental research on calcium and magnesium ion adsorption by applying the white carbon black [ D ] inner Mongolia university, 2015 ] use synthesized white carbon black as an adsorbent, the removal capacity of the white carbon black on magnesium ions in an aqueous solution under different conditions is investigated, and the saturated adsorption capacity is 11.58mg/g.
The above description is only a part of the embodiments of the present invention, but the scope of the present invention is not limited thereto, and any changes or substitutions that can be easily conceived by those skilled in the art within the technical scope of the present invention are included in the scope of the present invention.

Claims (7)

1. A synthetic method of a magnetic coal gasification slag-based magnesium adsorbent is characterized by comprising the following steps:
step (1), mixing the coal gasification coarse slag and an electrolyte solution containing magnesium ions according to a solid-to-liquid ratio of 1:5-10 g/ml, placing the mixture into a plasma ball mill, and carrying out ball milling for 3-5h at the excitation voltage of 3-10kV and the rotating speed of 400-800 r/min;
transferring the product after ball milling treatment to a tubular reaction furnace, heating to 200-500 ℃, and reacting for 1-3h in a water vapor atmosphere;
and (3) enabling a reaction product obtained in the tubular furnace in the step (2) to react according to a solid-to-liquid ratio of 1:10-20 (g/ml) of the solution is soaked in a magnesium alginate and ferric amino acid solution, and a solid product is obtained by centrifugal separation after ultrasonic oscillation for 1-3 hours;
transferring the solid product to a tubular reaction furnace, heating to 300-600 ℃, and reacting for 1-5h in a water vapor atmosphere;
and (5) mixing the reaction product obtained in the step (4) according to a solid-liquid ratio of 1:5-10 (g/ml) of the magnetic gas slag-based magnesium adsorbent is immersed in 0.5-2mol/L of dilute acid solution, centrifugal separation is carried out after 0.5-2h of reaction, and drying is carried out to obtain the magnetic gas slag-based magnesium adsorbent.
2. The method for synthesizing the magnetic gasified slag-based magnesium adsorbent according to claim 1, wherein in the step (1), the electrolyte is one or more of magnesium hexafluorophosphate, magnesium perchlorate, magnesium tetrafluoroborate, magnesium hexafluoroarsenate, magnesium bistrifluoromethanesulfonylimide, perfluoroalkyl sulfonylmethyl magnesium, and magnesium difluorooxalato borate; the molar concentration of the electrolyte is 0.2-2mol/L.
3. The method for synthesizing the magnetic gasified slag-based magnesium adsorbent according to claim 1, wherein in the step (3), the solution is prepared in the following way: the molar concentration of the magnesium alginate is 3-5mol/L, the molar concentration of the ferric amino acid is 2-6mol/L, and the mixing volume ratio of the magnesium alginate to the ferric amino acid is 1:0.2-0.6.
4. The method for synthesizing the magnetic coal gasification slag-based magnesium adsorbent according to claim 1, wherein in the step (5), the dilute acid is one or more of hydrochloric acid, sulfuric acid and nitric acid.
5. The method for synthesizing the magnetic coal gasification slag-based magnesium adsorbent according to claim 1, wherein the specific surface area of the magnetic coal gasification slag-based magnesium adsorbent obtained in the step (5) is 300-500m 2 The pore diameter is 2-70nm, and the magnesium adsorption capacity is 30-60mg/g.
6. The magnetic coal gasification slag-based magnesium adsorbent is prepared by using the method for synthesizing the magnetic coal gasification slag-based magnesium adsorbent as claimed in any one of claims 1 to 6.
7. The method for extracting lithium from salt lake brine by using the magnetic gasified slag-based magnesium adsorbent as claimed in claim 6, wherein the method comprises the following steps:
s1, extracting magnesium in salt lake brine by using the magnetic coal gasification slag-based magnesium adsorbent to reduce the magnesium-lithium ratio;
s2, extracting lithium from the salt lake brine with the magnesium-lithium ratio reduced.
CN202210944379.6A 2022-08-07 2022-08-07 Synthesis method and application of magnetic coal gas slag-based magnesium adsorbent Active CN115254000B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202210944379.6A CN115254000B (en) 2022-08-07 2022-08-07 Synthesis method and application of magnetic coal gas slag-based magnesium adsorbent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202210944379.6A CN115254000B (en) 2022-08-07 2022-08-07 Synthesis method and application of magnetic coal gas slag-based magnesium adsorbent

Publications (2)

Publication Number Publication Date
CN115254000A true CN115254000A (en) 2022-11-01
CN115254000B CN115254000B (en) 2024-04-05

Family

ID=83749069

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202210944379.6A Active CN115254000B (en) 2022-08-07 2022-08-07 Synthesis method and application of magnetic coal gas slag-based magnesium adsorbent

Country Status (1)

Country Link
CN (1) CN115254000B (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN116850953A (en) * 2023-09-04 2023-10-10 山东中科瑞沃环境技术有限公司 Porous adsorption type sewage treatment material and preparation method thereof

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108607500A (en) * 2018-04-17 2018-10-02 成都新柯力化工科技有限公司 A kind of gel adsorber and preparation method carrying lithium for salt lake brine with high magnesium-lithium ratio
CN109266851A (en) * 2018-09-07 2019-01-25 中国科学院青海盐湖研究所 A method of lithium is extracted by magnetic micropore lithium adsorbent
CN110711559A (en) * 2018-07-12 2020-01-21 中国科学院宁波材料技术与工程研究所 Ion adsorbent and preparation method and application thereof

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108607500A (en) * 2018-04-17 2018-10-02 成都新柯力化工科技有限公司 A kind of gel adsorber and preparation method carrying lithium for salt lake brine with high magnesium-lithium ratio
CN110711559A (en) * 2018-07-12 2020-01-21 中国科学院宁波材料技术与工程研究所 Ion adsorbent and preparation method and application thereof
CN109266851A (en) * 2018-09-07 2019-01-25 中国科学院青海盐湖研究所 A method of lithium is extracted by magnetic micropore lithium adsorbent

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
何玉燕;: "改性锯屑对钙镁离子的吸附特性研究", 能源与环境, no. 2, 30 April 2009 (2009-04-30) *
冯华伟 等: "海藻酸钠-碳材料复合凝胶吸附水中污染物的研究进展", 《化工新型材料》, vol. 49, no. 3, 31 March 2021 (2021-03-31) *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN116850953A (en) * 2023-09-04 2023-10-10 山东中科瑞沃环境技术有限公司 Porous adsorption type sewage treatment material and preparation method thereof
CN116850953B (en) * 2023-09-04 2023-11-24 山东中科瑞沃环境技术有限公司 Porous adsorption type sewage treatment material and preparation method thereof

Also Published As

Publication number Publication date
CN115254000B (en) 2024-04-05

Similar Documents

Publication Publication Date Title
CN108439400A (en) A kind of N doping bagasse active carbon and preparation method thereof
CN115254000A (en) Synthetic method and application of magnetic coal gasification slag-based magnesium adsorbent
CN103706325A (en) Preparation method of lithium slag adsorbent for liquid extraction of lithium
CN110180489B (en) Sulfur-doped lithium-rich manganese lithium adsorbent and preparation method and application thereof
CN114272932A (en) Nickel-cerium biochar catalyst and preparation method and application thereof
CN110624548B (en) Preparation method of multistage iron oxide catalyst for removing heteroatoms in coal liquefied oil
CN112691666A (en) Amorphous iron oxyhydroxide-biochar composite material and preparation method thereof
CN109529757B (en) Preparation method of surface-doped long-life lithium ion sieve adsorbent
CN114452951B (en) Phenol formaldehyde aerogel rubidium/cesium specific adsorbent and preparation method and application thereof
CN113120902B (en) Preparation method of activated carbon
CN113289692B (en) Magnetic biomass solid catalyst and preparation and application thereof
CN111286060A (en) Preparation method of modified organic film for extracting lithium from seawater
CN112062127B (en) Coal-based nano porous carbon and preparation method thereof
CN111250034B (en) Modification method and application of desulfurization slag
CN112591798A (en) Preparation method of columnar manganese lithium ion sieve compound
CN115212844B (en) Composite adsorbent for extracting lithium from salt lake brine and preparation method thereof
KR20220140396A (en) Method for recovering and manufacturing crude lithium carbonate from the battery meterial raffinate
CN110790239B (en) Mechanical ball milling synthesis method of lithium sulfide powder
CN110711551A (en) Lithium adsorbent and preparation method thereof
CN114763264B (en) Process for preparing active carbon by alkali activation method
CN113332950B (en) Preparation method of lithium ion adsorbent and adsorbent precursor
CN116966871A (en) Preparation method of LiAl-LDHs/ZSM-5 composite lithium extraction material
CN109759013B (en) Cellulose-based lithium extraction material and preparation method thereof
CN114950354A (en) Uranium adsorbent based on porous cobalt sulfide/carbon aerogel material and preparation method thereof
CN115010141B (en) Method for preparing silicate by effectively utilizing salt lake potassium extraction byproduct bischofite

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant