CN106040239A - Controllable high-dispersion nano simple-substance metal/carbon composite material preparation method and electrical catalytic application thereof - Google Patents

Controllable high-dispersion nano simple-substance metal/carbon composite material preparation method and electrical catalytic application thereof Download PDF

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CN106040239A
CN106040239A CN201610358771.7A CN201610358771A CN106040239A CN 106040239 A CN106040239 A CN 106040239A CN 201610358771 A CN201610358771 A CN 201610358771A CN 106040239 A CN106040239 A CN 106040239A
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carbon
metal
preparation
nitrate
electrode
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CN106040239B (en
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滕玮
张伟贤
范建伟
冉献强
杨建平
吕梦华
许华伟
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Tongji University
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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
    • 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
    • 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
    • B01J23/75Cobalt
    • B01J35/50
    • 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
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • 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
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/467Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
    • C02F1/4676Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electroreduction
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia

Abstract

The invention relates to a controllable high-dispersion nano simple-substance metal/carbon composite material preparation method and electrical catalytic application thereof. An ordered mesoporous carbon powder material having high specific area is synthesized; the material is subjected to oxidation treatment to obtain mesoporous carbon provided with hydrophilic groups on the surface and having high specific area; metal precursor perfusion is performed by adopting an impregnation method, the mesoporous carbon is converted into hydroxide by adopting an ammonia fumigation method, and the hydroxide is fixed in mesoporous confined pore channels; reduction is performed at high temperature in the presence of H2, and finally a high-dispersion nano metal simple-substance/carbon composite material is obtained. With zero-valent iron/mesoporous carbon as an example, the composite material serves as a working electrode, a three-electrode electrochemical method is adopted to remove nitrate in a water body through electrical catalytic reduction. The composite material prepared by adopting the preparation method contains small simple-substance metal nanoparticles which are evenly dispersed in the pore channels of a carbon substrate, and the metal crystallization degree and supporting amount are easy to control in the preparation process. After electrode slices are produced, the nitrate treatment efficiency is high, the nitrogen selectivity is improved, the stability is good, and secondary pollution such as metal ion dissolution is not caused.

Description

A kind of high-dispersion nano metal simple-substance/carbon composite controllable method for preparing and electricity thereof Catalytic applications
Technical field
The invention provides and a kind of use electro-catalysis reduction to remove the nano composite material preparation method of nitrate in water body And application, belong to pollutant catabolic gene and remove field, relate to a kind of mesoporous carbon-loaded high-load, polymolecularity metal simple-substance nanometer The preparation method of granular materials.
Background technology
Along with economic fast development, the use of a large amount of chemical nitrogen fertilizers, life, industrial wastewater and the unreasonable place of mud Putting, in the surface water and groundwater of many countries and regions, nitrate content increases day by day, have become as one fairly common and Serious environmental problem.In natural water, the rising of nitrogen element can cause body eutrophication and break out wawter bloom, drinking water simultaneously The absorption of nitrate too much in source, can be converted into nitrite in human body, thus induce methemoglobinemia, sternly Hypoxia death can be caused during weight.World Health Organization (WHO) specifies NO in drinking water in water quality standard for drinking water3-N concentration is less than 10 mg/L.Therefore, effectively control and process the water source of high azotate pollution and become the task of top priority.
The method of nitrate in water body of removing at present mainly has physics, chemistry and bioanalysis.For comparing, Physical goes Not there is selectivity except nitrate, the most real degraded of pollutant, simply there occurs transfer or concentrate;The conventional anti-nitre of biology Nitrate transformation is nitrogen by the reduction of microorganism by change method, but the method capacity of resisting impact load is poor, complex process, There is secondary pollution problems simultaneously;Chemical reduction method mainly includes metal simple-substance reducing process, catalysis reduction and electrochemical process.Gold Belong to simple substance reducing process to be mainly with metal simple-substances such as ferrum, aluminum, zinc as reducing agent, have problems in that the product of reaction is difficult to turn Turn to harmless nitrogen, and the secondary pollution of metal ion etc. can be produced.And be catalyzed reduction using monometallic or bimetallic as Catalyst reduces nitrate, but typically requires use hydrogen as reducing agent, and hydrogen dissolubility at ambient pressure is little, uses peace Full property is the best.Electrochemical reducing utilizes electronics for reducing agent, obtains the extensive concern of research worker in recent years.Generally electrochemistry Often it is used in combination with noble metal catalyst, and electrochemical method is used in combination the application carrying out catalysis reduction with base metal simple substance Still there is potentiality to be exploited.
Ferrum is a kind of metal cheap and easy to get.Nano zero valence iron, because its particle size is little, reducing activity strong, the most extensively should The research of all kinds of pollutant removals in water body.In conjunction with nano zero valence iron and the advantage of electrochemical method, use nitre simultaneously Hydrochlorate carries out being catalyzed reduction can work in coordination with its removal ability of raising.Yet with big specific surface and magnetic, nano zero valence iron is non- Chang Rongyi reunites, and greatly reduces its effective active position, and during be there is certain nanometer in the environment in material release Toxicity.Therefore nano zero valence iron is supported on certain carrier, thus can high degree of dispersion nano-particle with prevent reunite, increase Add its specific surface and active sites, metal can be fixed again and reduce secondary pollution.Ordered mesoporous material is that a class aperture is at 2~50 nm Material, as novel nano material carrier, have its unique advantage.Especially ordered mesoporous carbon material, has big ratio table Area and pore volume, pore-size distribution homogeneous and on nanoscale continuously adjustabe, pore passage structure is from one-dimensional adjustable and advise to three-dimensional Then orderly, morphology controllable, framing structure is stable, advantages of environment protection.Mesoporous carbon is highly stable in water body, its mesopore orbit Can load, disperse and fix the nano-metal particle of even particle size as the confinement space of nano-particle.It addition, carbon Material is a kind of good conductive material.Nano zero valence iron granule uniform load, in the duct of mesoporous carbon, can be formed simultaneously Micropartical electrode.By this compound negative electrode making electrode, collaborative simple substance catalysed reductive energy and chemical property, thus improve right The clearance of nitrate and selectivity, avoid secondary pollution problem simultaneously.
With mesoporous carbon for the research of support dispersion nano zero valence iron it has been reported that but obtain one by control synthesis and have Little granule and dispersed and that load capacity is high nano zero valence iron/meso-porous carbon material, be still that a problem with challenge. For angle prepared by material, nano zero valence iron generally (is had the reagent such as NaBH of strong reducing power by liquid-phase reduction4), carbon heat Reduction, vapour phase reduction (reducibility gas such as H2), pyrogenic metal predecessor Fe (CO)5Obtain etc. method.For nano zero valence iron Load, the method using vapour phase reduction is a preferable method of loading.It addition, anti-during vapour phase reduction of ferrum predecessor Answering process can cause a certain degree of predecessor Species migration and reunion, the introducing that therefore need nonetheless remain for certain technology improves dispersion Performance.
Summary of the invention
It is an object of the invention to provide the nano metal simple substance/carbon of a kind of polymolecularity, good stability, high reaction activity Composite, as a example by nano zero valence iron/mesoporous carbon, makes electrode slice by this composite, in conjunction with electrocatalytic denitrification method, reduction Remove the nitrate in water body.
Nano metal simple substance/the mesoporous carbon composite material of preparation proposed by the invention, is provided stable and can by mesoporous carbon The carrier of conduction, has big specific surface area;Simultaneously because the confinement effect in mesoporous carbon duct, elemental metals particle size is equal One, crystallization degree can be controlled by sintering temperature and time, and tenor is adjustable between 1 ~ 70 wt%.
A kind of high-dispersion nano metal simple-substance/carbon composite controllable method for preparing that the present invention proposes, concrete steps are such as Under:
(1) synthesis has the order mesoporous carbon powder material of high-ratio surface;
(2) oxidant is configured to solution, the order mesoporous carbon powder material mix and blend obtained with step (1), 30~120 DEG C Under water-bath, stir 0.5~24 hour;Cooling, filtration;It is vacuum dried at 60 DEG C, obtains the meso-porous carbon material of surface oxidation;
(3) meso-porous carbon material of surface oxidation step (2) obtained disperses in ethanol;Metal precursor is dissolved in simultaneously Ethanol is configured to the solution of 20 wt%;Then both the above solution mixed, stir, make metal precursor be impregnated into mesoporous carbon In material duct, until ethanol volatilization is dry in fume hood;The meso-porous carbon material being filled with metal precursor obtained is put into In cuvette, cuvette is placed in the politef bottle equipped with 14 wt% ammonia spirits, keeps solid sample and ammonia It is not directly contacted with, seals latter 60 DEG C and process 3 hours;Remove sample surfaces solubilized impurity with water and washing with alcohol, filtration, obtain Load the meso-porous carbon material of this metal hydroxides;
(4) meso-porous carbon material of metal hydroxides step (3) obtained is put in tube furnace, H2/N2Atmosphere at high temperature roasts Burn, obtain nano metal simple substance/mesoporous carbon composite material.
In the present invention, the order mesoporous carbon powder material described in step (1) is: the FDU series of soft template method synthesis The one of CMK series (CMK-3, CMK-5) etc. of (FDU-14, FDU-15, FDU-16, FDU-18) or hard template synthesis or several Kind, or one or several in activated carbon or CNT.
In the present invention, described in step (2), oxidant is the one in nitric acid, hydrogen peroxide, potassium permanganate or Ammonium persulfate. Or several, the concentration of described oxidant is 0.5~2 M(0.5~the acidifying of 2.0 M sulphuric acid).
In the present invention, metal precursor described in step (3) is the one of ferric nitrate, cobalt nitrate, nickel nitrate;Nano metal The load capacity of simple substance by changing the addition of metal precursor or can be obtained by secondary or three perfusion control.
In the present invention, after metal precursor is impregnated in the duct of meso-porous carbon material by step (3), ammonia fumigating need to be used Steaming is translated into the hydroxide of metal and is fixed in described duct.
In the present invention, H used in step (4)2/N2Being the nitrogen atmosphere containing 10% hydrogen under atmosphere, high-temperature roasting temperature is 200~600 DEG C, roasting time is 0.5~4 h, controls H2/N2Gas flow rate is 25~200 mL/min, heating rate is 1 °/ min。
In the present invention, the specific surface area of the nano metal simple substance/carbon composite prepared is 600~1200 cm3/ G, metal nanoparticle is single zero-valent state simple substance, and is dispersed in mesoporous carbon confinement duct, metal nanoparticle particle diameter It is 3~8 nm.
Nano metal simple substance/the carbon composite that preparation method of the present invention obtains application in electro-catalysis is reduced, As a example by Zero-valent Iron/carbon composite, nano zero valence iron/carbon composite is made working electrode, use three-electrode electro Chemical Method, by the nitrate pollutants in electro-catalysis reduction water body.
In the present invention, described working electrode is according to Zero-valent Iron/carbon composite: white carbon black: be dissolved in N-crassitude The PVDF(10 g/L of ketone) the ratio mix homogeneously of=80 wt%:10 wt%:10 wt%, coat nickel foam (1 cm × 1 cm) On, baking oven 40~60 DEG C are dried 4~8 hours, and in vacuum drying oven, 120~140 DEG C are dried 8~12 hours, under 20 Mpa pressure Compacting obtains;The consumption coating the composite on working electrode is 3~5 mg, platinum electrode as to electrode, saturated calomel Electrode is reference electrode;Voltage-0.4~-4.0 V, reacts 1~24 hour.
In the present invention, containing nitrate initial concentration in described water body is 20~500 mg/L, and electrolyte is sodium chloride, sulfur One or more in acid sodium, hydrochloric acid or sodium hydroxide, pH value is 2~13.
The present invention has the advantages that and is:
(1) the invention provides the preparation method of a kind of nano metal simple substance/mesoporous carbon composite material.This preparation method is by adopting With having high-ratio surface, the mesoporous carbon of duct three-dimensional communication is as supporting substrate, by rear perfusion metal precursor ammonification again The method of hydrogen reducing, obtains high capacity amount, high degree of dispersion, granular size stable homogeneous, the adjustable composite of tenor.
(2) present invention is using nano zero valence iron/carbon composite as the negative electrode of electrochemistry, it is provided that this kind of applicating cooperation profit By the catalysis reduction of base metal simple substance and the advantage of electrochemical reduction, improve the removal effect of nitrate pollutants in water body Rate.
(3) above-mentioned composite is during electro-catalysis reduction nitrate, and reactivity is high, the selectivity to nitrogen Height, good stability, difficult drop-off, decrease the generation of secondary pollution.
Accompanying drawing explanation
Transmission electron microscope (TEM) photo of Fig. 1 nano zero valence iron/mesoporous carbon composite material, is prepared by embodiment 2.
The recycling performance of nitrate is removed in Fig. 2 nano zero valence iron/mesoporous carbon composite material electro-catalysis reduction, uses reality Execute example 8 material to obtain.
Detailed description of the invention
The present invention is further illustrated below by embodiment.
Embodiment 1
Phenolic resin and the preparation of surface oxidation ordered mesoporous carbon material: first 12.0 g phenol are melted in 40~42 DEG C of water-baths Melt, add 2.52 g 20%(mass percentage concentration) NaOH aqueous solution, stir 10 minutes, add 20.4 g formalins (37 wt%), at 70~75 DEG C, back flow reaction 1 hour, is cooled to room temperature.PH value of solution is regulated to neutral with the HCl of 0.6 M.Will This solution system is placed in 45 DEG C of water-baths decompression distillation 1~2 hour, obtains 14.1 g phenolic resin (molecular weight 200~500). It is dissolved in 56.2 g dehydrated alcohol, centrifugal segregation NaCl crystal, is configured to the light brown phenolic aldehyde tree that mass fraction is 20% Fat performed polymer ethanol solution, standby.By 1.6 g nonionic surfactant poly(ethylene oxide)-poly(propylene oxide)-polycyclic oxygen second Alkane triblock copolymer (Pluronic F127) and 1.0 g 0.2 M HCl join in 8.0 g ethanol, stir l at 40 DEG C Hour obtain settled solution.It is subsequently adding 2.08 g tetraethyl orthosilicates and the phenolic resin performed polymer second of 5.0 g 20 wt% Alcoholic solution, and continue to stir 2 hours.Transferring in glass culture dish by the yellow solution of mix homogeneously, ambient temperatare is put and is waved Send out 8 hours, be dried through 100 DEG C, cooling.The orange-yellow thin-film material obtained is scraped from culture dish, after suitably grinding, at nitrogen It is heated to 900 DEG C with 2 DEG C/min under gas atmosphere and keeps 2 hours.The black powder obtained is immersed in 10 wt%'s of excess In HF solution, it is stirred overnight, removes silica component, mesoporous through filtering, wash and obtain after drying the powder of high-ratio surface Material with carbon element.Then 1.0 M H are configured2SO41 M salpeter solution of acidifying, is mixed and stirred for the meso-porous carbon material obtained, 30 Stirring in water bath 6 hours at DEG C, filter.It is vacuum dried at 60 DEG C, finally gives the powder meso-porous carbon material of surface oxidation.
Embodiment 2
The preparation of the loaded mesoporous material with carbon element of Zero-valent Iron: by the meso-porous carbon material dispersed with stirring of 0.6 g surface oxidation at 8.0 g ethanol In;Simultaneously by 0.9 g Fe (NO3)3·9H2O dissolves and is configured to the solution that mass fraction is 20 wt% in ethanol, and adds 0.5 mL 0.2 M HCl suppresses Fe (NO3)3·9H2The hydrolysis of O.The solution dissolved is joined the alcoholic dispersion system of carbon, Continue stirring, until ethanol volatilization is dry in fume hood.Putting in cuvette by the composite obtained, glass tubing is placed in dress Have in the politef bottle of 14 wt% ammonia spirits, keep sample to be not directly contacted with ammonia, seal rear 60 DEG C of process 3 little Time, cooling, remove sample surfaces solubilized impurity with water and washing with alcohol, filtration, obtain loading Fe (OH)3Mesoporous carbon material Material.This composite is put into vacuum drying oven 60 DEG C be dried, place into tube furnace, pure H2/N2(1:10) the lower 400 DEG C of roastings 2 of atmosphere Hour, finally obtain Zero-valent Iron/mesoporous carbon composite material (resulting materials transmission electron microscope is shown in Fig. 1).
Embodiment 3
The preparation of the loaded mesoporous material with carbon element of cobalt: preparation method such as embodiment 2, except that add 1.0 in material preparation process g Co(NO3)3·9H2O dissolves and is configured to the solution that mass fraction is 20 wt% in ethanol
Embodiment 4
Electro-catalytic process removes nitrate: first nano zero valence iron/mesoporous carbon composite material is made working electrode.By composite wood Material, white carbon black and the PVDF(10 g/L being dissolved in N-Methyl pyrrolidone) it is thoroughly mixed into black slurry by the mass ratio of 8:1:1, Coating (1 cm × 1 cm) in nickel foam, put into 40 DEG C of baking oven and be dried 5 hours, placing in vacuum drying oven 120 DEG C, to be dried 8 little Time, suppress 2 minutes under 20 Mpa pressure, obtain working electrode sheet.Material about 3 mg/cm of coating on electrode2.Platinum electrode is made For to electrode, saturated calomel electrode is reference electrode, uses three-electrode method, processes the waste water containing nitrate.Water distribution is 100 Mg/L nitrate nitrogen, 0.02 mol/L sodium chloride.Electrochemistry denitration reaction is carried out under-1.3 V voltages, after reacting 24 hours, inspection Survey the NO in solution3 -、NO2 -And NH4 +, the clearance of nitrate, N can be calculated2Conversion ratio and unit mass composite Process capacity (the results are shown in Table 1).
The preparation of embodiment 5 nano zero valence irons/carbon composite and this composite is removed as electrode catalyst reduction The method of nitrate such as embodiment 1,2,4 in water except that in material preparation process the sintering temperature of hydrogen be 600 DEG C, roasting 1 hour burning time.
Embodiment 6
The preparation of nano zero valence iron/carbon composite and this composite is removed nitrate in water as electrode catalyst reduction Method such as embodiment 1,2,4 except that during in material preparation process, the load capacity of ferrum is embodiment 2 1/3rd, i.e. 0.3 g Fe(NO3)3·9H2O dissolves and is configured to the solution that mass fraction is 10 wt% in ethanol.
Embodiment 7
The preparation of nano zero valence iron/carbon composite and this composite is removed nitrate in water as electrode catalyst reduction Method such as embodiment 1,2,4 is except that removing water distribution during nitrate is 50 mg/L nitrate nitrogens.
Embodiment 8
The preparation of nano zero valence iron/carbon composite and this composite is removed nitrate in water as electrode catalyst reduction Method such as embodiment 1,2,4, except that remove during nitrate, reuses same working electrode sheet, be electrolysed 4 times with Obtain recycling performance;During removal nitrate, water distribution is 50 mg/L nitrate nitrogen (see figure 2)s.
Table 1 is to be that in embodiment 4-7, the removal of the nano zero valence iron/carbon composite electrochemical reduction nitrate of preparation is imitated Rate, N2Selectivity and unit mass thereof remove capacity.
Table 1
Embodiment Clearance (%) N2Selectivity (%) Remove capacity (mg/g)
Embodiment 4 30.5 85 435
Embodiment 5 33.5 82 340
Embodiment 6 16.8 65 64
Embodiment 7 29.5 75 235
The above-mentioned description to embodiment is to be understood that for ease of those skilled in the art and apply the present invention.Ripe These embodiments obviously easily can be made various amendment by the personnel knowing art technology, and described herein the most former Ought to use in other embodiments without through performing creative labour.Therefore, the invention is not restricted to embodiment here, ability Field technique personnel should be the present invention's according to the announcement of the present invention, the improvement made without departing from scope and amendment Within protection domain.

Claims (10)

1. high-dispersion nano metal simple-substance/carbon composite controllable method for preparing, it is characterised in that specifically comprise the following steps that
(1) synthesis has the order mesoporous carbon powder material of high-ratio surface;
(2) oxidant is configured to solution, the order mesoporous carbon powder material mix and blend obtained with step (1), 30~120 DEG C Under water-bath, stir 0.5~24 hour;Cooling, filtration;It is vacuum dried at 60 DEG C, obtains the meso-porous carbon material of surface oxidation;
(3) meso-porous carbon material of surface oxidation step (2) obtained disperses in ethanol;
(4) metal precursor dissolving is configured in ethanol the solution of 20 wt%;
(5) solution step (3) and step (4) obtained mixes, stirring, makes metal precursor be impregnated into meso-porous carbon material duct In, until ethanol volatilization is dry in fume hood, obtain being filled with the meso-porous carbon material of metal precursor;
(6) putting in cuvette by the meso-porous carbon material being filled with metal precursor that step (5) obtains, cuvette is placed in In politef bottle equipped with 14 wt% ammonia spirits, keep solid sample to be not directly contacted with ammonia, seal at latter 60 DEG C Manage 3 hours;Remove sample surfaces solubilized impurity with water and washing with alcohol, filtration, obtain loading Jie of this metal hydroxides Hole material with carbon element;
(7) meso-porous carbon material of metal hydroxides step (6) obtained is put in tube furnace, H2/N2Atmosphere at high temperature roasts Burn, obtain nano metal simple substance/mesoporous carbon composite material.
Preparation method the most according to claim 1, it is characterised in that: the order mesoporous carbon dust material described in step (1) Material is: one or several of the FDU series of soft template method synthesis or the CMK series of hard template synthesis, or activated carbon or carbon receives One or several in mitron.
Preparation method the most according to claim 1, it is characterised in that: described in step (2), oxidant is nitric acid, dioxygen One or several in water, potassium permanganate or Ammonium persulfate., the concentration of described oxidant is 0.5~2 M.
Preparation method the most according to claim 1, it is characterised in that: metal precursor described in step (3) be ferric nitrate, Cobalt nitrate, the one of nickel nitrate;The load capacity of nano metal simple substance is by changing the addition of metal precursor or by two Secondary or three perfusion control obtains.
Preparation method the most according to claim 1, it is characterised in that: metal precursor is impregnated into by step (3) mesoporous After in the duct of material with carbon element, ammonia need to be used to fumigate and to be translated into the hydroxide of metal and be fixed in described duct.
Preparation method the most according to claim 1, it is characterised in that: H used in step (4)2/N2It is containing 10% hydrogen under atmosphere The nitrogen atmosphere of gas, high-temperature roasting temperature is 200~600 DEG C, and roasting time is 0.5~4 h, controls H2/N2Gas flow rate is 25 ~200 mL/min, heating rate is 1 °/min.
Preparation method the most according to claim 1, it is characterised in that: the nano metal simple substance/carbon composite wood prepared The specific surface area of material is 600~1200 cm3/ g, metal nanoparticle is single zero-valent state simple substance, and is dispersed in mesoporous carbon In confinement duct, metal nanoparticle particle diameter is 3~8 nm.
8. nano metal simple substance/carbon composite that arbitrary preparation method obtains in a kind such as claim 1-7 is in electro-catalysis also Application in former, it is characterised in that: nano zero valence iron/carbon composite is made working electrode, uses three-electrode electro Chemical side Method, by the nitrate pollutants in electro-catalysis reduction water body.
Application the most according to claim 8, it is characterised in that: described working electrode is according to Zero-valent Iron/carbon composite: White carbon black: be dissolved in the PVDF(10 g/L of N-Methyl pyrrolidone) the ratio mix homogeneously of=80 wt%:10 wt%:10 wt%, it is coated with Being distributed in nickel foam (1 cm × 1 cm), baking oven 40~60 DEG C are dried 4~8 hours, in vacuum drying oven 120~140 DEG C be dried 8~ 12 hours, suppress under 20 Mpa pressure and obtain;The consumption coating the composite on working electrode is 3~5 mg, platinum electricity Pole is as to electrode, and saturated calomel electrode is reference electrode;Voltage-0.4~-4.0 V, reacts 1~24 hour.
Application the most according to claim 8, it is characterised in that: in described water body containing nitrate initial concentration be 20~ 500 mg/L, electrolyte is one or more in sodium chloride, sodium sulfate, hydrochloric acid or sodium hydroxide, and pH value is 2~13.
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CN110280300A (en) * 2019-06-13 2019-09-27 中国科学技术大学 A kind of preparation method and application loading Mn oxide ordered mesoporous carbon composite material
CN111170308A (en) * 2020-01-19 2020-05-19 贵州中医药大学 Method for preparing spherical hydrophilic nano mesoporous carbon material by chitosan-F127 binary system
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