CN106881059B - A kind of preparation method of iron/carbon composite - Google Patents

A kind of preparation method of iron/carbon composite Download PDF

Info

Publication number
CN106881059B
CN106881059B CN201710064168.2A CN201710064168A CN106881059B CN 106881059 B CN106881059 B CN 106881059B CN 201710064168 A CN201710064168 A CN 201710064168A CN 106881059 B CN106881059 B CN 106881059B
Authority
CN
China
Prior art keywords
iron
carbon
source
preparation
carbon composite
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN201710064168.2A
Other languages
Chinese (zh)
Other versions
CN106881059A (en
Inventor
李文卫
王丹丹
柳后起
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.)
Suzhou Institute for Advanced Study USTC
Original Assignee
Suzhou Institute for Advanced Study USTC
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 Suzhou Institute for Advanced Study USTC filed Critical Suzhou Institute for Advanced Study USTC
Priority to CN201710064168.2A priority Critical patent/CN106881059B/en
Publication of CN106881059A publication Critical patent/CN106881059A/en
Application granted granted Critical
Publication of CN106881059B publication Critical patent/CN106881059B/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
    • 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
    • B01J23/74Iron group metals
    • B01J23/745Iron
    • 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
    • B01J20/20Solid 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
    • 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
    • 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
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • 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
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/02Specific form of oxidant
    • C02F2305/026Fenton's reagent

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Analytical Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Inorganic Chemistry (AREA)
  • Water Supply & Treatment (AREA)
  • Materials Engineering (AREA)
  • Processing Of Solid Wastes (AREA)
  • Carbon And Carbon Compounds (AREA)

Abstract

The present invention relates to field of material technology, specifically disclose a kind of preparation method of iron/carbon composite, and the present invention prepares iron/carbon composite using the method that hydro-thermal method-co-precipitation-galvanoplastic combine for the first time.Synthesis process can be analyzed to two steps: firstly, the organic matter raw material added with molysite is carbonized using hydro-thermal method;Second, product after carbonization is restored using reducing agent appropriate, to obtain required iron/carbon composite.Mainly with the fixed surface and inside for being present in porous carbon materials of zeroth order Iron activiation, carbon material serves not only as the substrate of load Zero-valent Iron but also plays a certain protective role to Zero-valent Iron ferro element in the iron/carbon material obtained using this method.Therefore, the composite material of synthesis had both had the good reducing power of Zero-valent Iron, it may have carbon material is to the good adsorption capacity of organic pollutant, to realize the more efficient removal of organic pollutants.

Description

A kind of preparation method of iron/carbon composite
Technical field
The present invention relates to field of material technology, are to be related to a kind of iron/carbon composite more specifically.
Background technique
Iron/carbon composite is a kind of widely used, new material for haveing excellent performance, is widely used in photocatalysis material The fields such as material, electrode material, sensor, sewage treatment.Currently, the synthetic method of the material mainly have arc process, ion beam method, Laser method, chemical vapour deposition technique, high-temperature heat treatment method and Low Temperature Thermal solution.Difference can be synthesized using these preparation methods Iron/carbon composite of particle size, different shape.But these generally existing costs of iron/carbon composite synthetic method The disadvantages of high, complicated for operation.Such as: arc process needs special arc discharge device and pure raw material, but the production obtained Produce amount is seldom;Chemical vapour deposition technique needs to use special experimental provision and synthesis takes a long time;High-temperature heat treatment method At least 1500 DEG C or more of high temperature is needed, therefore not only energy consumption is high, time-consuming but also more demanding to laboratory apparatus.
In order to solve the above technical problems, the present invention comes therefrom.
Summary of the invention
Invention to be designed to provide a kind of raw material sources extensive, it is at low cost, be suitble to iron/carbon composite wood of large-scale promotion Material and preparation method thereof, iron/carbon composite of synthesis can be used for removing environmental contaminants.
In order to solve these problems in currently available technology, the technical solution that first aspect present invention provides is a kind of Iron/carbon composite preparation method comprising following steps:
(1) hydro-thermal method carbonization raw material
It chooses organic carbon source and dissolubility trivalent iron salt is source of iron, after organic carbon source cleaning pretreatment, by carbon ferro element Organic carbon source and source of iron are added in reaction kettle than the ratio for 10:1-20:1, and suitable water is added by organic carbon source and iron Source is sufficiently mixed, and under certain temperature and time, obtains carbonized product;
(2) co-precipitation-galvanoplastic reduction step (1) product
Carbonized product obtained in step (1) is cleaned with water, and is scattered in water phase, then addition and ferro element The reducing agent of the amount of equal substances, stands a period of time;
(3) separation of iron/carbon composite and post-processing
Product obtained in step (2) is separated by solid-liquid separation, solid product is washed with water, is then dried in vacuo, finally Obtain iron/carbon composite.
Preferably, organic carbon source is selected from carbohydrate, and further, organic carbon source is selected from monosaccharide or polysaccharide, further, described to have Machine carbon source is selected from glucose or rice husk agricultural organic waste or its mixing.
Preferably, the dissolubility trivalent iron salt is selected from ferric nitrate, ferric sulfate, iron chloride.
Preferably, in step (1), reaction kettle is placed in steel kettle, heating reaction is carried out.
Preferably, in step (1), well-mixed organic carbon source and source of iron are in 160-220 DEG C of temperature, reaction time 8-18 Under the conditions of hour, carbonized product is finally obtained.
Preferably, the reducing agent in step (2) is selected from sodium borohydride.
Preferably, in step (2) at room temperature, the reduction with the amount of the substances such as ferro element is slowly added dropwise while stirring Agent.
Preferably, vacuum drying is 8-24 hours dry at 60 DEG C of vacuum oven in the step (3).
A kind of preparation method of iron/carbon composite provided by the invention comprising following steps:
(1) hydro-thermal method carbonization raw material
Suitable carbon source and source of iron are selected first.It can use the agriculture organic waste such as the Organic Ingredients such as glucose or rice husk Object is carbon material, is source of iron with dissolubility trivalent iron salt.After carbon source cleaning pretreatment, (carbon is mixed with source of iron according to a certain percentage Ferro element ratio is 10:1-20:1), it then feeds the mixture into reaction kettle, and suitable water is added and is sufficiently mixed, it will be anti- Answer temperature control at 180 DEG C or so, the reaction time is 8-18 hours;
(2) co-precipitation-galvanoplastic reduction step (1) product
Carbonized product obtained in step (1) is cleaned with water and is scattered in water phase, side is stirred at room temperature Mix side be slowly added to the reducing agent of the amount of the substances such as ferro element (sodium borohydride, NaBH4), be then allowed to stand about 0.5-2 hours;
(3) separation of iron/carbon composite and post-processing
Product obtained in step (2) is separated by solid-liquid separation, solid product is cleaned multiple times with water remaining to remove Reactant is then placed in vacuum oven, at least 8 hours dry at a temperature of 60 DEG C, and iron/carbon composite can be obtained.
The present invention prepares iron/carbon composite using the method that hydro-thermal method-co-precipitation-galvanoplastic combine for the first time.It closes It can be analyzed to two steps at process: firstly, the organic matter raw material added with molysite is carbonized using hydro-thermal method;Second, Product after carbonization is restored using reducing agent appropriate, to obtain required material.
Present invention mainly discloses a kind of inexpensive, simple and practical and environmentally friendly iron/carbon composite preparation methods. Compared with traditional one-step method for synthesizing, the present invention in preparation method be divided into two steps progress, the reaction temperature needed it is lower and It is easy to operate.The first step uses hydrothermal synthesis method, and reaction temperature is only about 180 DEG C.Co-precipitation-electroplating reaction in second step exists It carries out at room temperature, therefore not only reduces operation energy consumption and reduce the risk of operation.In addition, this method can be adapted for Starch, carbohydrate, cellulose and the gas chromatography raw material (including abandoned biomass) containing these substances, can significantly reduce original Material cost even may be implemented to turn waste into wealth, these all significantly improve the economic and technical feasibility of large-scale industrial production, ring Border friendly and sustainability.
Ferro element is mainly present in porous carbon with the fixation of zeroth order Iron activiation in the iron/carbon material obtained using this method The surface and inside of material, carbon material serve not only as the substrate of load Zero-valent Iron but also play certain protection work to Zero-valent Iron With.Therefore, the composite material of synthesis had both had the good reducing power of Zero-valent Iron, it may have carbon material is good to organic pollutant Adsorption capacity, to realize the more efficient removal of organic pollutants.While ferro element of its load is during the reaction It can be released slowly, therefore not will cause the waste of ferro element and form a large amount of iron cements.Finally, the method for the present invention will be utilized Iron/carbon composite of synthesis is applied in Fenton advanced oxidation system, to achieve the purpose that efficiently to remove pollutant in water body.
Detailed description of the invention
Fig. 1 is the flow chart of preparation method of the present invention.
Fig. 2 is iron/carbon composite of preparation method of the present invention synthesis.Fig. 2 (a) is the material synthesized with rice husk as carbon source Material, Fig. 2 (b) are the material that carbon source synthesis is made of glucose.
Fig. 3 (a, b) is shown using glucose as iron/carbon composite scanning electron microscope (SEM) phenogram of carbon source.
Fig. 4 shows the iron/carbon composite synthesized using different carbon source ferrous ion (Fe at different pH2+) dissolution feelings Condition.
Fig. 5 shows the effect based on iron/carbon composite Fenton process removal sulfamethazine.
Specific embodiment
Above scheme is described further below in conjunction with specific embodiment.It should be understood that these embodiments are for illustrating The present invention and be not limited to limit the scope of the invention.Implementation condition used in the examples can be done according to the condition of specific producer Further adjustment, the implementation condition being not specified is usually the condition in routine experiment.
It introduces and summarizes
The present invention by way of example rather than provide the mode of limitation to be illustrated.It should be noted that in present disclosure " one " or "an" embodiment is not necessarily referring to same specific embodiment, and refers at least a kind of.
Various aspects of the invention are described below.However, as will be readily apparent to one of skill in the art, it can Only some or all of aspects according to the present invention implement the present invention.For purposes of illustration, provide herein specific number, material and Configuration, enables one to thoroughly understand the present invention.However, those of skill in the art are evident that, The present invention is without concrete details, that is, implementable.In other examples, many institutes have been omitted or simplified not make the present invention obscure Known feature.
Various operations are successively described as multiple discrete steps, and with the side of the invention most helpful in understanding Formula illustrates;However, in-order description should not be construed as to imply that these operations are necessarily dependent on sequence.
It will illustrate various embodiments according to the reactant of type species.Those of skill in the art will be shown and It is clear to, any number of different types of reactant can be used to implement for the present invention, and be more than those for the purpose of illustration And the reactant provided herein.In addition, also it is evident that, the invention is not limited to any specific mixing to show Example.
1 iron of embodiment/carbon composite preparation method
(1), hydro-thermal method carbonization organic matter
The rice husk for taking 2g carries out the impurity that removal surface is cleaned multiple times with water, then dries at 60 DEG C or so;It will be by pre- The raw material of processing is added in the polytetrafluoroethylene (PTFE) autoclave that dischargeable capacity is 25mL, while the nitric acid of 0.005mol is added Iron (Fe (NO3)3·9H2O) solid is added 15mL deionized water, is then sufficiently stirred, is sufficiently mixed reactant, due to The density of rice husk is small, it is easy to it floats on above solution, therefore rice husk should be thoroughly impregnated in clear water before the reaction, it can be abundant Dispersion in the liquid phase, will install the autoclave of reactant additional steel kettle again, which is put into electric drying oven with forced convection In, 180 DEG C are set by reaction temperature, controls the reaction time appropriate: 8 hours when rice husk is carbon source.
(2), product obtained in co-precipitation-galvanoplastic reduction step 1
Product obtained in step 1 is filtered, obtained solid matter is cleaned three times with deionized water, then will Solid product is put into vacuum oven at 80 DEG C 6 hours dry.Solid product 1.5g after taking out drying is added to reaction In device, and the deionized water of 200mL is added, ultrasound 5 minutes keeps solid particle fully dispersed in water, same what is be stirred continuously When, by the sodium borohydride (NaBH of 100mL 0.6mol/L4) solution is added dropwise in reactor, after being added dropwise to complete, stops stirring It mixes and stands 1 hour.
(3), the collection of iron/carbon composite and characterization
After the completion of step 2, reaction product is filtered rapidly, and three are cleaned to obtained solid with deionized water Time, then by the solid product cleaned up be put into vacuum oven 60 DEG C dry 8 hours or more, can be obtained desired Material.
Embodiment 2
The step only uses 0.01mol glucose as carbon source with embodiment 1, and hydro-thermal method carbonization organic matter walks Suddenly in (1), the reaction time is 12 hours.
As it is clear from fig. 2 that iron/the carbon material synthesized by carbon source of rice husk is shiny black color, the basic primary morphology for keeping rice husk; It is then in black powder using iron/carbon material that glucose is synthesized as carbon source.
One, scanning electron microscope (SEM) and power spectrum (EDS) characterization of material.
Iron/the carbon composite synthesized using glucose as carbon source is taken, material is pre-processed before characterization.It takes a small amount of It lightly, is equably sprinkled upon on the conducting resinl for being used for testing, then blows the conducting resinl with stream of nitrogen gas by synthetic product The extra material not with conducting resinl contact is blown away on surface.Material characterization result after pretreatment is as shown in Figure 3.
SEM figure shows that some iron is grown with spherical shape in carbon-based bottom surface, some iron is longer than in carbon substrate with spherical shape Portion, EDS chart confirm the presence of iron and carbon into one.Table 1 is shown using glucose as iron/carbon composite of carbon source EDAX results.Mainly it is demonstrated by the element contained in it and shared ratio.
Table 1
Element Wt% At%
C 03.21 07.98
O 03.52 06.56
S 89.31 83.01
Ti 03.96 02.46
Two, ferrous ion (Fe2+) dissolution experiment.
Iron/carbon composite the 20mg obtained using different carbon source (glucose or rice husk) synthesis is taken, its is evenly dispersed In the solution of pH=3, pH=7, pH=10 of 50mL, the pH value of solution is adjusted using dilute hydrochloric acid or diluted sodium hydroxide solution Section.It is sampled after reaction 0 minute, 30 minutes, 60 minutes and 120 minutes respectively.Then every sub-sampling 1mL tests the solution Central Asia Iron ion (Fe2+) concentration.Experimental result is as shown in Figure 4.In 30 minutes quickly, explanation is carried on the burst size of ferrous ion The iron of carbon-based bottom surface, which is largely dissolved in water body, becomes ferrous ion, gradually weakens and tends towards stability after 30 minutes, illustrates point Iron of the cloth inside carbon substrate gradually dissolves out.The result illustrates that iron/carbon composite of synthesis can within the scope of very wide pH Enough slow release ferrous ions, so as to the height for providing ferrous ion constantly for subsequent Fenton's reaction process to guarantee pollutant Effect stablizes degradation.
Three, the organic pollutant in water removal is removed using iron/carbon composite that embodiment 1,2 synthesizes
The composite material of 20mg synthesis is added into the aqueous solution containing 20mg/L sulfamethazine, and is added 20 μ L hydrogen peroxide constitutes Fenton's reaction system.Monitoring reactor reacts the pollutant removal situation after 2h under condition of different pH. Organic matter removal effect is as shown in Figure 5.The removal rate of sulfamethazine is 60%-80%, illustrates that iron/carbon of synthesis is compound Material can be applied to Fenton's reaction system within the scope of very wide pH and obtain preferable contaminant degradation effect, but in acidity Under the conditions of effect it is more preferable.In addition, comparison can be seen that with iron/carbon composite that different carbon source obtains, using rice husk as the iron of carbon source/ Carbon composite generally has higher removal efficiency.This explanation is synthesized using agricultural solid residues such as rice husks as carbon source Iron/carbon composite has wide development and application prospect
Specific embodiment described above is only the preferred embodiment of the present invention, it is noted that for the art For those of ordinary skill, without departing from the principle of the present invention, several improvement or replacement can also be made, these improvement Or replacement should also be as being considered as protection scope of the present invention.

Claims (5)

1. a kind of preparation method of iron/carbon composite comprising following steps:
(1) hydro-thermal method carbonization raw material
It chooses organic carbon source and dissolubility trivalent iron salt is source of iron, after organic carbon source cleaning pretreatment, be by carbon ferro element ratio Organic carbon source and source of iron are added in reaction kettle the ratio of 10:1-20:1, and suitable water is added and fills organic carbon source and source of iron Divide mixing, reaction kettle is placed in steel kettle, heating reaction is carried out;Well-mixed organic carbon source and source of iron are in temperature 160- 220 DEG C, under the conditions of reaction time 8-18 hour, finally obtain carbonized product;The organic carbon source is selected from rice husk agricultural organic waste Gurry;
(2) co-precipitation-galvanoplastic reduction step (1) product
Carbonized product obtained in step (1) is cleaned with water, and is scattered in water phase, is then added and the objects such as ferro element The reducing agent of the amount of matter stands a period of time;
(3) separation of iron/carbon composite and post-processing
Product obtained in step (2) is separated by solid-liquid separation, solid product is washed with water, is then dried in vacuo, finally to obtain the final product To iron/carbon composite.
2. preparation method according to claim 1, which is characterized in that the dissolubility trivalent iron salt is selected from ferric nitrate, sulphur Sour iron, iron chloride.
3. preparation method according to claim 1, which is characterized in that the reducing agent in step (2) is selected from sodium borohydride.
4. preparation method according to claim 1, which is characterized in that in step (2), at room temperature, while stirring The reducing agent with the amount of the substances such as ferro element is slowly added dropwise.
5. preparation method according to claim 1, which is characterized in that vacuum drying is in vacuum oven in step (3) It is 8-24 hours dry at 60 DEG C.
CN201710064168.2A 2017-02-04 2017-02-04 A kind of preparation method of iron/carbon composite Active CN106881059B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710064168.2A CN106881059B (en) 2017-02-04 2017-02-04 A kind of preparation method of iron/carbon composite

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710064168.2A CN106881059B (en) 2017-02-04 2017-02-04 A kind of preparation method of iron/carbon composite

Publications (2)

Publication Number Publication Date
CN106881059A CN106881059A (en) 2017-06-23
CN106881059B true CN106881059B (en) 2019-10-08

Family

ID=59178809

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710064168.2A Active CN106881059B (en) 2017-02-04 2017-02-04 A kind of preparation method of iron/carbon composite

Country Status (1)

Country Link
CN (1) CN106881059B (en)

Families Citing this family (17)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106861623B (en) * 2017-04-07 2019-08-30 郑州大学 A kind of carbon material and its preparation method and application of load C o-Fe alloy
CN107456984B (en) * 2017-09-04 2020-01-31 山东师范大学 Iron-carbon composite material with hydrogen production performance by visible light photolysis of water and preparation method thereof
CN107470338A (en) * 2017-09-30 2017-12-15 青岛农业大学 The in-situ remediation method and system of plasticiser and heavy metal lead pollution agricultural land soil
CN107442565A (en) * 2017-09-30 2017-12-08 青岛农业大学 A kind of method and device of in-situ immobilization polycyclic aromatic hydrocarbon polluted farmland soil
CN107597825A (en) * 2017-09-30 2018-01-19 青岛农业大学 The method and system of in-situ chemical and Co-bioremediation polycyclic aromatic hydrocarbon pollution
CN107470339A (en) * 2017-09-30 2017-12-15 青岛农业大学 The method and system of polycyclic aromatic hydrocarbon pollution is repaired in class Fenton and microorganism combination
CN107413840A (en) * 2017-09-30 2017-12-01 青岛农业大学 The in-situ remediation method and system of heavy metal cadmium and polycyclic aromatic hydrocarbon polluted farmland soil
CN107617635A (en) * 2017-09-30 2018-01-23 青岛农业大学 The class Fenton restorative procedure in situ and system of phthalic acid ester and As polluted soil
CN108355610A (en) * 2018-02-09 2018-08-03 河南工业大学 A kind of method of the preparation of mesoporous carbon-loaded zero-valent iron composite material and sulfamethazine of degrading applied to activation persulfate
CN108326323A (en) * 2018-03-29 2018-07-27 洛阳理工学院 A kind of preparation method of rice husk carbon load nanometer nulvalent iron particle
CN108936194A (en) * 2018-07-24 2018-12-07 武汉轻工大学 Colloid carbon ball/nano zero-valence iron composite material preparation method, food deoxidant and preparation method thereof
CN109065310A (en) * 2018-08-27 2018-12-21 合肥学院 A kind of magnetic carbon composite material preparation process
CN109692667A (en) * 2019-02-11 2019-04-30 南京林业大学 A kind of biomass arsenic removal material and preparation method thereof
CN109939680B (en) * 2019-03-28 2021-01-01 南开大学 Biochar-loaded zero-valent iron composite material and preparation method thereof
CN110220766B (en) * 2019-06-21 2021-10-22 辽宁石油化工大学 Method for quantitatively collecting phenol in water environment through composite material
CN115703058A (en) * 2021-08-04 2023-02-17 中国石油天然气股份有限公司 Iron-carbon nano composite and preparation method and application thereof
CN115739083A (en) * 2022-10-17 2023-03-07 东南大学 Hydrothermal carbon catalyst, preparation method thereof and preparation method of primary imine compound

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102125844A (en) * 2010-01-15 2011-07-20 复旦大学 Method for preparing iron-carbon microsphere material and use thereof
CN102784913A (en) * 2012-07-26 2012-11-21 天津大学 Hydrothermal preparation method of carbon-coated iron nanoparticles
CN106044921A (en) * 2016-06-20 2016-10-26 昆明理工大学 Preparation method and application of carbon sphere loaded nanoscale zero valent iron composite material

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US8668831B2 (en) * 2009-04-25 2014-03-11 Liberty Hydro, Inc. Method for contaminant removal from aqueous solution

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102125844A (en) * 2010-01-15 2011-07-20 复旦大学 Method for preparing iron-carbon microsphere material and use thereof
CN102784913A (en) * 2012-07-26 2012-11-21 天津大学 Hydrothermal preparation method of carbon-coated iron nanoparticles
CN106044921A (en) * 2016-06-20 2016-10-26 昆明理工大学 Preparation method and application of carbon sphere loaded nanoscale zero valent iron composite material

Also Published As

Publication number Publication date
CN106881059A (en) 2017-06-23

Similar Documents

Publication Publication Date Title
CN106881059B (en) A kind of preparation method of iron/carbon composite
CN109292883B (en) Graphitized biochar and method for degrading organic pollutants in water body by graphitized biochar
JP6801844B2 (en) Catalytic material for catalytically activating persulfate and targeting and decomposing typical pollutants in paper wastewater, its synthesis method and application
CN106076335B (en) A kind of preparation method and application of heterogeneous Fenton catalyst
CN106362690A (en) Magnetic biochar adsorbing material and preparation method thereof
CN108940376B (en) Surface organic complexing copper sulfide Fenton catalyst and synthetic method and application thereof
CN113877581A (en) Copper ferrite spinel material and preparation method and application thereof
CN112675893A (en) Method for preparing monatomic catalyst by using adsorbed-resolved waste adsorbent
CN114226721B (en) Graphite carbon coated nano zero-valent iron composite material and preparation method and application thereof
CN113318740B (en) Cu 2 O/MgFe 2 O 4 Catalyst, preparation method and application thereof
CN113332990B (en) Perovskite catalytic material and green synthesis method and application thereof
CN111068731A (en) Multielement carbon nitride based non-metallic material, preparation method and application thereof
CN113666479A (en) Application of crystal face controllable bismuth oxybromide catalyst in selective oxidative degradation of pollutants
CN107686156B (en) A kind of Fenton method of efficient degradation organic pollutants
CN111871417A (en) Mesoporous nanorod catalyst and preparation method and application thereof
CN115353189B (en) Method for treating ciprofloxacin-containing wastewater by regulating and controlling dissolved oxygen
CN114146689B (en) Aluminum/cerium bimetal organic framework material, preparation method and application thereof in adsorption dephosphorization
CN114471546B (en) Nano silver/biochar photocatalytic material and preparation method and application thereof
CN114849708A (en) Three-dimensional macroporous carbon anchored monatomic iron catalyst, and preparation method and application thereof
CN110182884B (en) Method for treating electroplating wastewater by catalytic decomplexation-adsorption of electroplating sludge and decomplexation-adsorption dual-functional material
CN107188167B (en) A method of active sludge carbon is prepared using activated by urine municipal sludge
CN112808289A (en) Alginate-based metal monatomic catalyst and preparation method and application thereof
CN115254024B (en) Preparation method of porous nano carbon sphere adsorbent for adsorbing hydrogen sulfide
CN109201002A (en) Transition metal carbide composite material, preparation method and its absorption purposes of a kind of charcoal package
CN115888717B (en) Charcoal loaded nano CoOOH catalyst for efficiently activating persulfate and preparation method thereof

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