CN105314726B - A kind of processing method of dyeing and printing sewage - Google Patents

A kind of processing method of dyeing and printing sewage Download PDF

Info

Publication number
CN105314726B
CN105314726B CN201410311123.7A CN201410311123A CN105314726B CN 105314726 B CN105314726 B CN 105314726B CN 201410311123 A CN201410311123 A CN 201410311123A CN 105314726 B CN105314726 B CN 105314726B
Authority
CN
China
Prior art keywords
based amorphous
dyeing
amorphous alloy
printing sewage
alloy powder
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
CN201410311123.7A
Other languages
Chinese (zh)
Other versions
CN105314726A (en
Inventor
霍军涛
甘卓然
常春涛
李润伟
王新敏
门贺
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.)
Ningbo Institute of Material Technology and Engineering of CAS
Original Assignee
Ningbo Institute of Material Technology and Engineering of CAS
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 Ningbo Institute of Material Technology and Engineering of CAS filed Critical Ningbo Institute of Material Technology and Engineering of CAS
Priority to CN201410311123.7A priority Critical patent/CN105314726B/en
Publication of CN105314726A publication Critical patent/CN105314726A/en
Application granted granted Critical
Publication of CN105314726B publication Critical patent/CN105314726B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Powder Metallurgy (AREA)
  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)

Abstract

The invention provides a kind of processing method of dyeing and printing sewage.This method selects the ferrous alloy raw material with AMORPHOUS ALLOY RIBBONS Forming ability, is prepared as ferrum-based amorphous alloy strip, then brittle, crushing, obtains Fe-based amorphous alloy powder, by the Fe-based amorphous alloy powder for dyeing and printing sewage processing.Compared with the conventional method, Fe-based amorphous alloy powder not only has higher specific surface area, and the Fe-based amorphous alloy powder and when being reacted to dyeing and printing sewage, its surface can form nano-porous structure, the nano-porous structure not only further increases the specific surface area of the Fe-based amorphous alloy, and can play a part of adsorbing azo dyes and reaction product during the course of the reaction, so as to substantially increase the treatment effeciency of dyeing and printing sewage.

Description

A kind of processing method of dyeing and printing sewage
Technical field
The present invention relates to dyeing and printing sewage processing technology field, and in particular to a kind of processing method of dyeing and printing sewage.
Background technology
Water process is the eternal problem of the mankind.With China's economic development, national water consumption rises year by year, and discharge of wastewater is total Amount increases, and increased wastewater emission amount causes the increase of water process pressure year by year.Textile industry is the traditional pillar industry in China, " three wastes " discharged in dyeing production process, especially waste water, environment will be caused seriously to pollute if improvement is improper. According to incompletely statistics, dyeing waste water daily discharge capacity in China's is 400~600 ten thousand steres.Dyeing waste water has water big, organic The features such as pollutant concentration is high, colourity is deep, alkalescence is high, change of water quality is big, complicated component, belong to industrial wastewater difficult to deal with it One.
Traditional sewage water treatment method is such as sterilized, purified, the high strength chemical processing of desalination can solve many pollutions and ask Topic.However, these methods are generally required for consuming substantial amounts of manpower and energy, and can only be by needing substantial amounts of fund, work Larger processing system that journey technology and infrastructure are supported and realize, therefore many places can not all make to carry out dirt in this way Water process, hamper its promotion and application worldwide.In addition, the chemical treatment of high intensity (such as is related to ammonia, chlorination Thing, hydrochloric acid, sodium hydroxide, ozone, potassium permanganate, alum and molysite, coagulating agent and help and consider agent, the corrosion control such as antisludging agent chemistry Medicament, and ion exchange resin and regenerative agent etc. chemical treatment) and its residue (sludge, bittern, toxic waste etc.) all can Become a source of fresh water pollution and salinization of soil.
In recent years, iron/water micro electrolysis tech is used for sewage disposal, and this method, which almost can be used in handling, all can not give birth to Change the waste water of processing, while can also water-borne pathogens be played with killing action, and ferro element reserves in the earth's crust are huge, valency Lattice are cheap, and this method without strong oxidizer, therefore is considered as a kind of environment-friendly processing without additional equipment in addition Method.At present, iron powder and cast iron scrap have been widely used in the processing of dyeing waste water.
But during reduced iron powder processing dyeing waste water, there are the following problems:(1) iron powder is often business and mark Brick;Compared with reduced iron powder, the index such as the purity of cast iron scrap, activity is poor, results in the need for longer processing time and can be only achieved The standard of subsequent treatment;(2) this method be there are certain requirements to the pH value of dyeing waste water, and this is just needed to large batch of printing and dyeing Waste water carries out pH value adjustment, causes practical application inconvenient;(3) there is serious hardened problem in iron/water light electrolysis;Using receiving It is both to possess bigger specific surface area although rice iron powder can prevent hardened to a certain degree, the manufacture of nanometer iron powder is difficult Degree is very high, it is difficult to industrialized production is realized, it is with high costs;(4) because reduced iron powder and cast-iron scrap are in actual dyeing waste water Serious oxidation can occur in processing procedure, cause the corrosion of iron to consume, and due to iron easily with acid reaction, by pickling and The poor operability of the recovery of its surface reduction ability is realized, the recycling to reduced iron powder or cast iron scrap brings difficulty, past Toward wastewater treatment of progress is only capable of, the cost rise of this method is caused, limits its extensive use.
In order to make up dyeing waste water handle using reduced iron powder or cast iron scrap existing treatment conditions it is more, Treatment effect is bad, and the shortcomings of repeatable usability difference, Fe base amorphous ribbons are made by amorphization techniques in scientific research personnel, The research using Fe bases amorphous ribbon processing dyeing waste water is carried out.Iron exists with atomic state in Fe base noncrystal alloys, remains What Zero-valent Iron had in itself removes color function, and has Fe-based amorphous and strip sample advantage concurrently, is a kind of good printing and dyeing water Except color material.But the efficiency of Fe bases amorphous ribbon processing dyeing and printing sewage is still relatively low, is not met by dyeing and printing sewage processing Actual demand.
The content of the invention
For the above-mentioned state of the art, the present invention is intended to provide a kind of new method of dyeing and printing sewage processing, this method are simply easy OK, it is higher to the treatment effeciency of dyeing and printing sewage.
In order to realize above-mentioned technical purpose, the present invention has carried out many experiments exploration.One of which method is:Utilizing During iron/water micro electrolysis tech is handled dyeing and printing sewage, Fe base amorphous ribbons are replaced with Fe-based amorphous alloy powder.Should Method is intended to improve the specific surface area of Fe-based amorphous alloy, so as to improve the treatment effect of dyeing and printing sewage.But using this method When, present inventors have surprisingly found that:Fe base amorphous ribbons are replaced with Fe-based amorphous alloy powder, it is non-iron-based can not only to be effectively improved The specific surface area of peritectic alloy, and the Fe-based amorphous alloy powder with the mistake of (degraded azo dyes) of being reacted to dyeing and printing sewage Cheng Zhong, surface can form nano-porous structure, and the nano-porous structure not only further increases the ratio of the Fe-based amorphous alloy Surface area, and play a part of adsorbing azo dyes and reaction product during the course of the reaction, it is dirty so as to substantially increase printing and dyeing The treatment effeciency of water.
That is, the technical scheme is that:A kind of processing method of dyeing and printing sewage, from ferrous alloy raw material, the iron-based Alloy raw material possesses ferrum-based amorphous alloy strip Forming ability;Raw material is prepared as ferrum-based amorphous alloy strip, after embrittlement processing Crush, obtained Fe-based amorphous alloy powder, its a diameter of 10 μm~200 μm;Fe-based amorphous alloy powder is used for dyeing and printing sewage Processing.
In the component of described Fe-based amorphous alloy, the atomic percent of iron is preferably between 60%~90% Preferably, to play the reduction-decolor ability of iron atom, other elements are unlimited, choose according to the actual requirements, can be Si, B, Nb, Cu, One kind in the element for advantageously forming Fe-based amorphous alloy that rare earth elements RE and existing literature and technical data are related to or It is several.
As a kind of implementation, the molecular formula of described Fe-based amorphous alloy is FeaSibBcMd, wherein subscript a, b, c, D represents the atomic percentage conc of corresponding element, and span is 60≤a≤90,0≤b≤20,5≤c≤30,0≤d≤30, and A+b+c+d=100.Wherein, element M be selected from the one kind of element such as Nb, Cu, Cr, Al, Mo, Ti, Zr, Pd, Ag, Au and rare earth or It is several.Preferably, the purity of Fe, Si, B and M element is not less than 99% (percentage by weight).For example, the Fe-based amorphous conjunction The molecular formula of gold is Fe78Si9B13、Fe77Si9B13La1、Fe73Si7B17Mo3、Fe73Si7B17Nb1Gd2、Fe75Si9B13Nb2Tb1、 Fe75Si9B13Tm3、Fe77Si9B13Y1Deng.
The method for preparing ferrum-based amorphous alloy strip using the ferrous alloy raw material is:Melting iron-based closes in electric arc furnaces Golden raw material, melting uniformly, after cooling obtain mother alloy ingot;Then, mother alloy ingot is sensed in induction melting furnace Molten metal, after substantially uniformity is molten into molten metal, is sprayed onto on the disk roller for get rid of carrying device and carries out getting rid of band by fusing by instantaneous differential pressure, Obtain ferrum-based amorphous alloy strip.According to the amorphous formation ability of ferrous alloy composition, the roller speed for getting rid of carrying device typically selects Select in 25~38m/s.
Described brittle processing method is unlimited, including carries out embrittlement using annealing process, and annealing temperature is less than Glass Transition Temperature.
Described breaking method is unlimited, and the Fe-based amorphous bar after embrittlement is brought into using the methods of ball milling, airflow milling Row crushes.
In summary, the present invention is prepared as from the ferrous alloy raw material with AMORPHOUS ALLOY RIBBONS Forming ability Ferrum-based amorphous alloy strip, then brittle, crushing, obtains Fe-based amorphous alloy powder, the Fe-based amorphous alloy powder is used for Dyeing and printing sewage processing.Compared with existing dyeing and printing sewage processing method, there is advantages below:
(1) Fe-based amorphous alloy powder exists with amorphous state, and on the one hand metastable amorphous state result is advantageous to improve iron The reactivity of atom, another aspect non-crystaline amorphous metal do not have crystal defect, the Zero-valent Iron in non-crystalline flour is not produced intergranular Corrosion and over oxidation, the corrosion consumption in wastewater treatment process again is effectively reduced, on the premise of decolorization rate is ensured Powder is reused, overcomes the technology and applied defect of traditional reduced iron powder or cast iron waste scrap dyeing waste water.
(2) Fe-based amorphous alloy exists with the state of powder, and compared with the shapes such as band, specific surface area greatly improves, and makes The utilization rate of iron atom is improved;Moreover, when the oxide and hydroxide deposition of the iron on non-crystaline amorphous metal powder surface are to necessarily Degree and when have impact on the treatment effect of powder, its decoloring ability is restored rapidly in a manner of pickling is washed away, Therefore reusing is good.
(3) the Fe-based amorphous alloy powder is in dyeing and printing sewage handles processing procedure, during azo dyes of degrading, table Face forms nano-porous structure, not only further increases its specific surface area, and plays absorption azo dyes and reaction production The effect of thing, so as to greatly improve the treatment effeciency of dyeing and printing sewage.
(4) experimental verification, the Fe-based amorphous alloy powder is excellent to the treatment effeciency of dyeing and printing sewage, its Degradation of Azo Dyes speed Rate is more than 50 times of traditional iron powder.
In addition, method provided by the invention is simple and easy, cost is low, without substantial contribution, Technical investment, therefore is printing and dyeing Had a good application prospect during the decolorization of waste water.
Brief description of the drawings
Fig. 1 is Fe made from embodiment 178Si9B13The stereoscan photograph and grain size analysis knot of Fe-based amorphous alloy powder Fruit is schemed;
Fig. 2 is the Fe in embodiment 178Si9B13Fe-based amorphous alloy powder and Fe78Si9B13Iron-based crystal alloy powder pair 200mg/L direct blue 2Bs aqueous dye solutions carry out the XRD spectrum before and after sewage disposal;
Fig. 3 is Fe in embodiment 178Si9B13Fe-based amorphous alloy powder and Fe78Si9B13Iron-based crystal alloy powder is to 200mg/ L direct blue 2Bs aqueous dye solutions carry out the outward appearance photo of solution in sewage disposal process;
Fig. 4 is iron powder, Fe in embodiment 178Si9B13Fe-based amorphous alloy powder and Fe78Si9B13Iron-based crystal alloy powder pair 200mg/L direct blue 2Bs aqueous dye solutions carry out the absorbance curve of solution in sewage disposal process;
Fig. 5 is iron powder, Fe in embodiment 178Si9B13Fe-based amorphous alloy powder and Fe78Si9B13Iron-based crystal alloy powder pair 200mg/L direct blue 2Bs aqueous dye solutions carry out iron powder, Fe after sewage disposal 7 minutes78Si9B13Fe-based amorphous alloy powder with Fe78Si9B13The SEM figures and specific surface area analysis result figure of iron-based crystal alloy powder.
Fig. 6 is Fe made from embodiment 277Si9B13La1The stereoscan photograph and grain size analysis knot of Fe-based amorphous alloy powder Fruit is schemed;
Fig. 7 is the Fe in embodiment 277Si9B13La1The XRD spectrum of Fe-based amorphous alloy powder;
Fig. 8 is iron powder and Fe in embodiment 277Si9B13La1Fe-based amorphous alloy powder is to 200mg/L direct blue 2B dyestuff water Solution carries out the absorbance curve of solution in sewage disposal process;
Fig. 9 is the Fe in embodiment 3-773Si7B17Mo3、Fe73Si7B17Nb1Gd2、Fe75Si9B13Nb2Tb1、 Fe75Si9B13Tm3、Fe77Si9B13Y1The XRD spectrum of Fe-based amorphous alloy powder;
Figure 10 is iron powder and Fe in embodiment 3-773Si7B17Mo3、Fe73Si7B17Nb1Gd2、Fe75Si9B13Nb2Tb1、 Fe75Si9B13Tm3、Fe77Si9B13Y1Fe-based amorphous alloy powder carries out sewage disposal to 200mg/L direct blue 2Bs aqueous dye solutions The absorbance curve of solution in journey.
Embodiment
Embodiment is described in further detail to the present invention below in conjunction with the accompanying drawings, it should be pointed out that implementation as described below Example is intended to be easy to the understanding of the present invention, and does not play any restriction effect to it.
Embodiment 1:
In the present embodiment, dyeing and printing sewage is the direct blue 2B dyestuff water that concentration is 200mg/L, utilizes Fe-based amorphous alloy powder Fe78Si9B13, iron-based crystal alloy powder Fe78Si9B13, and commercial iron powder handles the dyeing and printing sewage respectively.
(1) Fe-based amorphous alloy powder Fe78Si9B13Preparation
Fe78Si9B13It is a kind of composition for possessing stronger amorphous formation ability, Fe-based amorphous alloy powder Fe78Si9B13's Preparation method is as follows:
(1)Fe78Si9B13The preparation of foundry alloy
Using Fe, Si and B element that purity is not less than to 99% (percentage by weight) according to 78:9:13 atom ratio Dispensing, in the electric arc furnaces of the argon atmospher of titanium absorption, the raw mixture melting for preparing more than 3 times is well mixed, after cooling Obtain mother alloy ingot;
(2)Fe78Si9B13The preparation of Fe-based amorphous band
Using carrying device is got rid of, mother alloy ingot is subjected to induction melting using intermediate frequency power supply in an atmosphere, when fusing is complete When composition is uniform, by instantaneous differential pressure, instantaneous differential pressure is 0.03MPa in the present embodiment, and it is 30m/s's that molten metal is sprayed onto into rotating speed On copper roller, get rid of band and obtain amorphous ribbon, the width of the amorphous ribbon is 2mm, and thickness is 30 μm;
(3)Fe78Si9B13The preparation of Fe-based amorphous alloy powder
By Fe78Si9B13Fe-based amorphous band brittle annealing 1 hour, Ran Houli at the vacuum less than 0.003Pa, 400 DEG C Amorphous ribbon ball milling after being annealed with the ball mill of 400g zirconia balls to 25~30g 4 hours, every turn is stopped half an hour in one hour, The speed that revolves round the sun is 250 revs/min, obtains Fe78Si9B13Fe-based amorphous alloy powder, with after alcohol washes 5~6 times with 120 mesh, 200 Mesh, 320 mesh sieve are sieved into 160 μm, 80 μm, 30 μm or so three specifications.
Electron microscope experiment and grain size analysis are scanned to the Fe-based amorphous alloy powder of 30 μm of specifications.As shown in figure 1, the iron-based Amorphous powdered alloy is the uniform fine powder of 32.5 μm of particle mean size.
X-ray diffraction test is carried out to the Fe-based amorphous alloy powder of 30 μm of specifications, as shown in Fig. 2 confirming that the powder has been Full amorphous state.
(2) iron-based crystal alloy powder Fe78Si9B13Preparation
A part is taken out in the Fe-based amorphous alloy powder of 30 μm of specifications obtained above, is filled after being enclosed in pumping high vacuum Being annealed 45 minutes in the quartz ampoule of argon gas, at 600 DEG C makes water cooling after its complete crystallization, obtains Fe78Si9B13Iron-based crystal alloy Powder, for carrying out contrast experiment.
To the Fe78Si9B13Iron-based crystal alloy powder carries out X-ray diffraction test, as shown in Fig. 2 confirming the powder for crystalline substance State powder.
(3) use of commercial iron powder
The commercial iron powder of processing sewage typically requires that its iron content is more than or equal to 99%, and granularity is more than 40 mesh, and (i.e. diameter is small In 380 μm).In order to contrast the excellent sewage disposal performance of non-crystalline flour, the larger average grain of the present embodiment selection specific surface area Spend for 10 μm, purity be 99.9% iron powder as a comparison case.
(4) Fe-based amorphous alloy powder Fe is utilized78Si9B13, iron-based crystal alloy powder Fe78Si9B13And iron powder is printed Stain water process
Take Fe-based amorphous alloy powder Fe obtained above78Si9B13, iron-based crystal alloy powder Fe78Si9B13, and iron powder is each 2g, it is respectively put into the beaker for filling the direct blue 2B aqueous dye solutions that 150ml concentration is 200mg/L.Beaker is placed in constant temperature In water-bath, kept for 35 DEG C, decolorization 7 minutes, in processing procedure, after being spaced certain reaction time, take about 7ml solution respectively Sample is tested as follows:
(1) after the different disposal time, the outward appearance of the solution of Fe-based amorphous powder and crystalline state powder is put into as shown in figure 3, can be with , it is evident that Fe-based amorphous powder is substantially better than crystalline state powder for the decolorizing effect of direct blue 2B aqueous dye solutions.
(2) according to the relevant knowledge of spectroscopy, it is seen that absorbance pass proportional to solution concentration at light area maximum absorption band System, based on this, the change of solution concentration can be drawn by the variation tendency of absorbance at visible region maximum absorption band.
After the different disposal time, iron powder, Fe are put into78Si9B13Fe-based amorphous alloy powder and Fe78Si9B13Crystal alloy powder Solution absorbance curve it is as shown in Figure 4.As can be seen that Fe from the Fig. 478Si9B13Fe-based amorphous alloy powder is for direct The decolorization rate of blue 2B aqueous dye solutions will be significantly faster than that the Fe after crystallization78Si9B13The decolorization rate of iron-based crystal alloy powder;Together When can be seen that Fe78Si9B13Fe-based amorphous alloy powder is about commercial iron for the decolorization rate of direct blue 2B aqueous dye solutions 100 times or so of powder.
(3) after handling 7 minutes, the iron powder, Fe78Si9B13Fe-based amorphous alloy powder and Fe78Si9B13The table of crystal alloy powder Face microstructure and specific surface area test result are as shown in Figure 5.
As can be seen from Figure 5:The surface smoother of iron powder;Fe78Si9B13There was only some isolated islands in the surface of crystal alloy powder The particle of shape;And Fe78Si9B13During degradation treatment indigo plant 2B aqueous dye solutions, surface forms Fe-based amorphous alloy powder Nano-porous structure, the nano-porous structure not only can further increase the specific surface area of non-crystalline flour, and can play absorption The effect of azo dyes and reaction product, effect is handled to the colour of camel's hair of direct blue 2B aqueous dye solutions so as to greatly improve to have handled Rate.
(4) after handling 7 minutes, to Fe78Si9B13Fe-based amorphous alloy powder and Fe78Si9B13Crystal alloy powder carries out X ray Diffraction is tested, as shown in Fig. 2 confirming the Fe78Si9B13Fe-based amorphous alloy powder remains in that after degradable azo dyes Complete amorphous structure, illustrates the Fe78Si9B13It is even that Fe-based amorphous alloy powder can carry out recycling degraded well Nitrogen dyestuff.
Embodiment 2:
In the present embodiment, Fe is utilized77Si9B13La1Fe-based amorphous alloy powder handles the dyeing and printing sewage.
Fe-based amorphous alloy powder Fe in the present embodiment77Si9B13La1Preparation method it is substantially the same manner as Example 1, institute not Same is raw material Fe, Si, B and La element according to 77:9:13:1 atom ratio carries out dispensing.
Similar embodiment 1, to Fe77Si9B13La1Fe-based amorphous alloy powder is scanned electron microscope experiment and grain size analysis.Such as Shown in Fig. 6, the Fe-based amorphous alloy powder is the uniform fine powder of 29.2 μm of particle mean size.
Similar embodiment 1, the XRD of the Fe-based amorphous alloy powder in the present embodiment show that the alloy is amorphous alloy, As shown in Figure 7.
According to the method that dyeing and printing sewage is handled in embodiment 1, Fe-based amorphous alloy powder Fe obtained above is taken77Si9B13La1 Carry out the Decolorant Test of direct blue 2B aqueous dye solutions.Fe77Si9B13La1Fe-based amorphous alloy powder and iron powder processing different time Solution absorbance curve it is as shown in Figure 8.As can be seen that Fe from the Fig. 877Si9B13La1Fe-based amorphous alloy powder is for straight The decolorization rate of commercial iron powder will be significantly faster than that by connecing the decolorization rate of blue 2B aqueous dye solutions, be approximately its 100 times or so.
Embodiment 3-7:
In embodiment 3-7, Fe is utilized73Si7B17Mo3、Fe73Si7B17Nb1Gd2、Fe75Si9B13Nb2Tb1、Fe75Si9B13Tm3、 Fe77Si9B13Y1Fe-based amorphous alloy powder handles the dyeing and printing sewage.
Fe-based amorphous alloy powder Fe in the present embodiment73Si7B17Mo3、Fe73Si7B17Nb1Gd2、Fe75Si9B13Nb2Tb1、 Fe75Si9B13Tm3、Fe77Si9B13Y1Preparation method it is substantially the same manner as Example 1, except that each element is according to corresponding point The atom ratio of minor carries out dispensing.The particle mean size of five kinds of powder is between 20~40 μm.
Similar embodiment 1, the XRD of the Fe-based amorphous alloy powder in embodiment 3-7 show that these alloys are that amorphous state is closed Gold, as shown in Figure 9.
According to the method that dyeing and printing sewage is handled in embodiment 1, the Fe-based amorphous alloy powder in Example 3-7 carries out direct The Decolorant Test of blue 2B aqueous dye solutions.Fe-based amorphous alloy powder Fe73Si7B17Mo3、Fe73Si7B17Nb1Gd2、 Fe75Si9B13Nb2Tb1、Fe75Si9B13Tm3、Fe77Si9B13Y1Absorbance curve with the solution of iron powder processing different time is as schemed Shown in 10.As can be seen that the Fe-based amorphous alloy powder in embodiment 3-7 is for direct blue 2B aqueous dye solutions from the Figure 10 Decolorization rate will be significantly faster than that the decolorization rate of commercial iron powder, be approximately its 50~100 times or so.
Above-described embodiment is used for illustrating the present invention, rather than limits the invention, the present invention spirit and In scope of the claims, to any modifications and changes of the invention made, protection scope of the present invention is both fallen within.

Claims (8)

1. a kind of processing method of dyeing and printing sewage, it is characterized in that:From ferrous alloy raw material, the ferrous alloy raw material possesses iron-based AMORPHOUS ALLOY RIBBONS Forming ability;Raw material is prepared as ferrum-based amorphous alloy strip, crushes, is made Fe-based amorphous after embrittlement processing Alloy powder, its a diameter of 10 μm~200 μm;Fe-based amorphous alloy powder is added in dyeing and printing sewage to the mistake for carrying out sewage disposal Cheng Zhong, Fe-based amorphous alloy powder surface form nano-porous structure.
2. the processing method of dyeing and printing sewage as claimed in claim 1, it is characterized in that:The composition member of described Fe-based amorphous alloy In element, the atomic percent of iron is 60%~90%.
3. the processing method of dyeing and printing sewage as claimed in claim 1, it is characterized in that:Described ferrous alloy raw material prepares iron-based The method of AMORPHOUS ALLOY RIBBONS is:The melting ferrous alloy raw material in electric arc furnaces, melting uniformly, after cooling obtain foundry alloy casting Ingot;Then, mother alloy ingot is subjected to induction melting in induction melting furnace, after substantially uniformity is molten into molten metal, passes through wink When pressure difference molten metal be sprayed onto on the disk roller for get rid of carrying device carry out getting rid of band, obtain ferrum-based amorphous alloy strip.
4. the processing method of dyeing and printing sewage as claimed in claim 1, it is characterized in that:Brittle processing is carried out using annealing process.
5. the processing method of dyeing and printing sewage as claimed in claim 1, it is characterized in that:Using ball milling or airflow milling method to crisp Fe-based amorphous band after change is crushed.
6. the processing method of dyeing and printing sewage as claimed in claim 3, it is characterized in that:The described roller speed for getting rid of carrying device is 25~38m/s.
7. the processing method of the dyeing and printing sewage as described in any claim in claim 1 to 6, it is characterized in that:Described iron The molecular formula of base noncrystal alloy is FeaSibBcMd, wherein subscript a, b, c, d represent the atomic percentage conc of corresponding element, value Scope is 60≤a≤90,0≤b≤20,5≤c≤30,0≤d≤30, and a+b+c+d=100;Element M be selected from Nb, Cu, Cr, One or more in Al, Mo, Ti, Zr, Pd, Ag, Au and rare earth element.
8. the processing method of dyeing and printing sewage as claimed in claim 7, it is characterized in that:The molecular formula of described Fe-based amorphous alloy For Fe78Si9B13、Fe77Si9B13La1、Fe73Si7B17Mo3、Fe73Si7B17Nb1Gd2、Fe75Si9B13Nb2Tb1、Fe75Si9B13Tm3、 Fe77Si9B13Y1
CN201410311123.7A 2014-07-01 2014-07-01 A kind of processing method of dyeing and printing sewage Active CN105314726B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410311123.7A CN105314726B (en) 2014-07-01 2014-07-01 A kind of processing method of dyeing and printing sewage

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410311123.7A CN105314726B (en) 2014-07-01 2014-07-01 A kind of processing method of dyeing and printing sewage

Publications (2)

Publication Number Publication Date
CN105314726A CN105314726A (en) 2016-02-10
CN105314726B true CN105314726B (en) 2017-12-12

Family

ID=55243159

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410311123.7A Active CN105314726B (en) 2014-07-01 2014-07-01 A kind of processing method of dyeing and printing sewage

Country Status (1)

Country Link
CN (1) CN105314726B (en)

Families Citing this family (22)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106006916B (en) * 2016-07-18 2020-01-07 中国科学院金属研究所 Method for degrading coking wastewater by using iron-based amorphous alloy
CN106986474A (en) * 2017-04-05 2017-07-28 深圳大学 A kind of device for being used to handle azo dyes sewage
CN107119223A (en) * 2017-04-11 2017-09-01 深圳大学 It is a kind of for the material and preparation method of sewage disposal and application
CN107176668A (en) * 2017-04-11 2017-09-19 深圳大学 It is a kind of for the material and preparation method of sewage disposal and application
CN107326159B (en) * 2017-06-20 2019-08-16 清华大学 A kind of iron-base nanometer crystal alloy methods for making and using same and device for being handled containing azo dye printing and dyeing wastewater
CN109304470B (en) * 2017-07-28 2020-07-10 华中科技大学 Surface-modified amorphous zero-valent iron, and preparation method and application thereof
CN109402369A (en) * 2017-08-15 2019-03-01 南京理工大学 A kind of iron-based porous material and preparation method thereof for azo dyes of degrading
CN109399765B (en) * 2017-08-16 2022-02-01 南京理工大学 Method for electrochemically degrading azo dye wastewater by using amorphous alloy
CN109399779B (en) * 2017-08-16 2022-02-01 南京理工大学 Application of iron-based amorphous/graphene oxide composite material in degradation of azo dyes
CN107538014A (en) * 2017-08-22 2018-01-05 东莞市联洲知识产权运营管理有限公司 A kind of preparation method of iron-based nanometer heterogeneous alloy powder containing transition element and its application in azo dye wastewater processing
CN107445281A (en) * 2017-08-28 2017-12-08 北京科技大学 It is a kind of to be used to handle non-crystaline amorphous metal net of dyeing waste water and preparation method thereof
CN108220824B (en) * 2017-12-15 2021-05-14 华南理工大学 Iron-based amorphous alloy strip and application thereof in degradation treatment of printing and dyeing wastewater
CN108525688A (en) * 2018-04-28 2018-09-14 东南大学 A kind of Fe-based amorphous alloy is used for the application of degradation of dye waste water Methylene Blue
CN108821346B (en) * 2018-05-31 2021-04-02 清华大学 Preparation method and application of iron oxide with three-dimensional flower-like nano structure
CN109434120B (en) * 2018-11-14 2021-09-03 东南大学 Iron-based amorphous alloy powder for degrading dye waste liquid and preparation method and application thereof
CN109440023B (en) * 2018-12-26 2019-10-18 中国科学院宁波材料技术与工程研究所 A kind of high magnetic strength nitrogen coupling Fe-based amorphous nanocrystalline alloy and preparation method thereof
CN109652746A (en) 2019-01-09 2019-04-19 王静然 A kind of amorphous band master alloy and preparation method thereof
CN110028146B (en) * 2019-04-11 2022-03-08 东南大学 Application of iron-based amorphous alloy in degradation of acid orange 7
CN110918911B (en) * 2019-11-19 2022-04-22 华南理工大学 Iron-based series amorphous alloy strip, preparation method thereof and application thereof in degradation of azo dye wastewater
CN111304558A (en) * 2020-04-08 2020-06-19 辽宁大学 Nano-porous coated Fe-based amorphous alloy and preparation method and application thereof
CN115414953B (en) * 2022-07-25 2023-10-20 郑州大学 Fe-P-C-B-Al amorphous/nanocrystalline alloy ribbon, preparation method thereof and application thereof in degradation of dye
CN115536123A (en) * 2022-11-01 2022-12-30 山东大学 Method for Fenton catalytic degradation of methylene blue sewage by FeBCCr amorphous alloy

Family Cites Families (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102070236B (en) * 2009-11-20 2012-11-14 中国科学院金属研究所 Application of ferrum-based amorphous alloy strip for treating printing and dyeing wastewater
KR101402891B1 (en) * 2011-03-08 2014-06-02 씨에그린 주식회사 Manufacturing method for Iron-based adsorbent
CN102383069A (en) * 2011-10-19 2012-03-21 无锡华冶钢铁有限公司 Iron-based amorphous alloy used for printing and dying wastewater treatment
CN102909363B (en) * 2012-10-18 2014-07-23 山东大学 Iron-base alloy compound material, preparation method thereof and method for disposing petroleum drilling wastewater
CN103219119A (en) * 2013-04-18 2013-07-24 安泰科技股份有限公司 Preparation method of mu90 high-permeability Fe-based amorphous magnetic powder core
CN103290342B (en) * 2013-06-19 2015-09-02 天津非晶科技有限公司 Fe base noncrystal alloy and preparation method thereof
CN103880149A (en) * 2014-03-20 2014-06-25 上海理工大学 Method of degrading dye wastewater by iron-based amorphous alloy/hydrogen peroxide Fenton-like system

Also Published As

Publication number Publication date
CN105314726A (en) 2016-02-10

Similar Documents

Publication Publication Date Title
CN105314726B (en) A kind of processing method of dyeing and printing sewage
JP4332591B2 (en) Method for recovering silica and then alumina from coal ash
CN103866127A (en) Method for preparing neodymium iron boron through regenerating waste material containing neodymium, iron and boron
CN101318656B (en) Metallurgy purification method for polysilicon
CN101293754B (en) Method for preparing titanium dioxide composite material with fine silica flour
Chen et al. Multi-phase nanocrystallization induced fast degradation of methyl orange by annealing Fe-based amorphous ribbons
CN110981202A (en) Microcrystalline glass and preparation method thereof
CN109402369A (en) A kind of iron-based porous material and preparation method thereof for azo dyes of degrading
CN114107668B (en) Method for mechanically activating, reinforcing and leaching rare earth in waste polishing solution
CN110284004A (en) A kind of method that copper ashes cooperates with recycling with sodium sulphate waste residue
CN104986773A (en) Purifying process for quartz raw materials for ultra-clear glass
Liu et al. Thorough extraction of lithium and rubidium from lepidolite via thermal activation and acid leaching
CN108190883A (en) A kind of method of purification of diamond
CN101875494B (en) Preparation method of low-titanium and high-purity polycrystalline silicon
CN108046402A (en) A kind of method using cu-based amorphous alloys degradation pigment wastewater
Quartarolli et al. Improving the lithium recovery using leached beta-spodumene residues processed by magnetic nanohydrometallurgy
CN112331474B (en) Recycling method of neodymium iron boron block waste
CN112209446B (en) Method for recycling Cr-containing tungsten carbide waste and application thereof
CN108840378A (en) Iron-absorbent charcoal composite material, method and application is prepared in situ in a kind of metallurgical dust
CN106268642A (en) Bobbles shape zinc oxide/graphene composite adsorbent and preparation method and application
CN104291340B (en) Method for removing phosphorus in industrial silicon
CN103123840B (en) A kind of permanent magnetic material with high compressive strength and preparation method thereof
CN115414953B (en) Fe-P-C-B-Al amorphous/nanocrystalline alloy ribbon, preparation method thereof and application thereof in degradation of dye
CN109847751A (en) It is a kind of to utilize metallurgical dust beam system for polynary magnetic iron base composite material, method and application
KR101572507B1 (en) A Method for Crushing Hard Tungsten Carbide Scraps under Non-oxygen Atmosphere

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant