CN106927695A - The low temperature closed-loop process technique of discarded glass - Google Patents

The low temperature closed-loop process technique of discarded glass Download PDF

Info

Publication number
CN106927695A
CN106927695A CN201710203766.3A CN201710203766A CN106927695A CN 106927695 A CN106927695 A CN 106927695A CN 201710203766 A CN201710203766 A CN 201710203766A CN 106927695 A CN106927695 A CN 106927695A
Authority
CN
China
Prior art keywords
glass
discarded
low temperature
defoamer
acid
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
CN201710203766.3A
Other languages
Chinese (zh)
Other versions
CN106927695B (en
Inventor
梁艳
岳秋林
王婷
赵林
李昆仑
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.)
Qilu University of Technology
Original Assignee
Qilu University of Technology
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 Qilu University of Technology filed Critical Qilu University of Technology
Priority to CN201710203766.3A priority Critical patent/CN106927695B/en
Publication of CN106927695A publication Critical patent/CN106927695A/en
Application granted granted Critical
Publication of CN106927695B publication Critical patent/CN106927695B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C03GLASS; MINERAL OR SLAG WOOL
    • C03CCHEMICAL COMPOSITION OF GLASSES, GLAZES OR VITREOUS ENAMELS; SURFACE TREATMENT OF GLASS; SURFACE TREATMENT OF FIBRES OR FILAMENTS MADE FROM GLASS, MINERALS OR SLAGS; JOINING GLASS TO GLASS OR OTHER MATERIALS
    • C03C25/00Surface treatment of fibres or filaments made from glass, minerals or slags
    • C03C25/70Cleaning, e.g. for reuse
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • CCHEMISTRY; METALLURGY
    • C03GLASS; MINERAL OR SLAG WOOL
    • C03CCHEMICAL COMPOSITION OF GLASSES, GLAZES OR VITREOUS ENAMELS; SURFACE TREATMENT OF GLASS; SURFACE TREATMENT OF FIBRES OR FILAMENTS MADE FROM GLASS, MINERALS OR SLAGS; JOINING GLASS TO GLASS OR OTHER MATERIALS
    • C03C25/00Surface treatment of fibres or filaments made from glass, minerals or slags
    • C03C25/64Drying; Dehydration; Dehydroxylation
    • CCHEMISTRY; METALLURGY
    • C03GLASS; MINERAL OR SLAG WOOL
    • C03CCHEMICAL COMPOSITION OF GLASSES, GLAZES OR VITREOUS ENAMELS; SURFACE TREATMENT OF GLASS; SURFACE TREATMENT OF FIBRES OR FILAMENTS MADE FROM GLASS, MINERALS OR SLAGS; JOINING GLASS TO GLASS OR OTHER MATERIALS
    • C03C25/00Surface treatment of fibres or filaments made from glass, minerals or slags
    • C03C25/66Chemical treatment, e.g. leaching, acid or alkali treatment

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Geochemistry & Mineralogy (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Processing Of Solid Wastes (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
  • Surface Treatment Of Glass Fibres Or Filaments (AREA)

Abstract

Present invention relates particularly to a kind of scrap glass fiber treatment technique.The low temperature closed-loop process technique of discarded glass of the invention, including:(1)The discarded glass of cleaning, dries;(2)Crush, obtain glass powder;(3)Impregnating active treatment;(4)Catalyst, defoamer, surfactant and solvent are placed in reactor and process;(5)Dry, calcining prepares glass fibre.The method of the present invention has exemplary role in field of the same trade, while also having huge Industry Effect power, can bring considerable economic benefit.The method of the present invention meets green production and sustainable development strategies, also complies with resource reclaim and recycles policy, and DEVELOPMENT PROSPECT is wide.

Description

The low temperature closed-loop process technique of discarded glass
Technical field
Present invention relates particularly to a kind of scrap glass fiber treatment technique.
Background technology
Glass fibre is a kind of Inorganic Non-metallic Materials of excellent performance, with quartz sand, pyrophyllite, lime stone, boric acid etc. Natural inorganic non-metallic ore is raw material, and by certain formula, through high temperature melting, wire drawing, doff etc., several technique is made, With high temperature resistant, anti-corruption, heat-insulated, tensile strength is high, and electrical insulating property waits well excellent properties, in electronic apparatus, auto industry, aviation Space flight, wind-power electricity generation and biomedicine field are used widely.But glass fibre belongs to fragile material, in order to strengthen its Mechanical property complies with process requirements, needs to be soaked in its surface coated glass fiber in the drawing process of production glass fibre Profit agent.Size can not only effectively lubricating glass fiber surface, moreover it is possible to by hundreds of or even thousands of glass monofilament integrated Beam, does not bond mutually between precursor after precursor is wound in cake.Increase glass fibre simultaneously soft during post-processing It is soft, reduce mechanical wear.Generally, the compositions such as film forming agent, coupling agent, lubricant, antistatic additive can be added in size, in glass Glass fiber surface forms a labyrinth layer for having concentration gradient.
Glass fiber waste silk is the industrial tailing of generation in glass fibre production, is a kind of solid waste, and China is annual 3~50,000 tons of waste silks for scribbling different type size will be produced, is a greatly burden for enterprise, for society Environmental pollution can more be caused.Choosing buried mode earliest carries out the treatment of waste silk, and the processing method causes the wave in a large amount of farmlands Take and pollute.As the control that Environmental is protected is more and more stricter, buried mode is eliminated completely, glass fibre production Enterprise needs the new method of searching badly to solve the problems, such as scrap glass fiber contamination.Most cheap, most environmentally friendly mode is at present Glass fibre is melted down again, but because the ratio when presence of size makes glass waste silk melt down again is unable to reach production Demand, therefore need to carry out the removal of size before melting down.The method of tradition removal size is high-temperature calcination, and temperature reaches 1400 DEG C, the method energy consumption it is higher and produce waste gas very big harm is caused to environment.Therefore seek energy consumption it is low, it is pollution-free removal leaching Profit agent method turns into glass fibre enterprise problem in the urgent need to address.
The content of the invention
It is low, pollution-free removal size to useless the invention provides a kind of energy consumption in order to solve above-mentioned technical problem Abandon the low temperature closed-loop process technique of glass.
Closed-loop process technique of the present invention, refers to take some specific handling process aborning, by what is produced Recovery and reuse of waste, externally without discharge(Zero-emission), pollution-free, the process that realization is recycled, so that reducing energy consumption, saves Cost, and favorable environment.
The low temperature closed-loop process technique of discarded glass of the invention, including:
(1)The discarded glass of cleaning, dries;
(2)Crush, obtain glass powder;
(3)The treatment of inorganic acid impregnating active;
(4)Catalyst, defoamer, surfactant and solvent are placed in reactor and process;
(5)Dry, calcining prepares glass fibre.
Discarded glass involved in the present invention includes epoxide resin type glass, unsaturated polyester type glass, acrylic ester type The discarded glasses such as glass, phenolic resin type glass, polyurethane-type glass.
Discarded glass being cleaned using the method being cleaned by ultrasonic, supersonic frequency is 30~100KHz, scavenging period is 1~ 15min;Glass waste silk after cleaning is in dry 2~10h at 80~120 DEG C.
Dried discarded glass is cut into short silk of the length less than 2mm, air-flow micronizer, air velocity is sent into It is the hypervelocity swirling eddy of more than 1.5MHZ, discharge pressure is 0.5~1.2MPa.
Inorganic acid impregnation process step specifically, pickling bath liquor pH value be 1~5, inorganic acid be hydrochloric acid, sulfuric acid, nitric acid, The mixture of one or more in phosphoric acid, hypochlorous acid, dichromic acid, perchloric acid, the addition of inorganic acid is glass powder gross weight The 3~10% of amount, the impregnating active time is 6~10h.
Above-mentioned catalyst includes Al2O3, KNO3/Al2O3, KOH/Al2O3, NaOH/ Al2O3, LiOH/ Al2O3, CsOH/ Al2O3, NaOH, KOH, LiOH, at least one in CsOH;
Solvent includes at least one in water, lower alcohol, organic alkane, ethers;
Surfactant is stearic acid, neopelex, stearyl dimethyl benzyl ammonium chloride, cetyl bromination At least one in ammonium, sorbierite surfactant;
Defoamer is organic silicon defoamer, polyethers defoamer, silicon and ether grafting class defoamer, defoamer containing amine, imines At least one of class defoamer and amide-type defoamer;
Glass powder after activation:Catalyst:Solvent:Surfactant:The quality parts ratio of defoamer is 20~30:3~8:80~ 100:0.5~1.2:0.1~0.8.
Preferably,(4)In reaction condition it is as follows:Under the conditions of 50~120 DEG C, pressure be 0.5~1MPa, stirring 4~ 12h, stir speed (S.S.) is 1000~3000r/min.
(5)Middle glass fibre evaporation, after reclaiming solvent for use, 1h~5h is dried at 100~250 DEG C, and kiln is returned after drying Calcining prepares glass fibre.
The present invention employs lossless, green, environment-friendly treating process for glass fiber treating compound removal.At present rarely have similar to This technology is realized industrialization by the documents and materials report of the inventive method, Ye Weiyou enterprises, and the method for the present invention is led in the same industry There is exemplary role in domain, while also having huge Industry Effect power, considerable economic benefit can be brought.The present invention Method meet green production and sustainable development strategies, also comply with resource reclaim and recycle policy, DEVELOPMENT PROSPECT is wide.
Brief description of the drawings
Fig. 1 is SEM measurement results after the inventive method treatment glass waste silk;
Fig. 2 is present invention process flow chart.
Specific embodiment
Come to be further described the present invention with reference to the accompanying drawings and detailed description, so as to the technology of this area Personnel know more about the present invention, but with this do not limit the present invention.
Heretofore described " part ", unless otherwise specified, refers both to parts by weight;
Embodiment 1
The low temperature closed-loop process technique of epoxide resin type glass fiber waste silk, comprises the following steps:
(1)Epoxide resin type glass fiber waste silk is cleaned by ultrasonic, supersonic frequency is 70KHz, scavenging period is 15min, Cleaning at 80 DEG C after drying 5h;
(2)Dried discarded glass cuts into the short silk of length 1mm or so, and air-flow ultramicro grinding is sent under air-flow drive Machine, air velocity is the hypervelocity swirling eddy of more than 1.8MHz, and discharge pressure is 0.6MPa, and 200 mesh sieves are crossed after crushing;
(3)Discarded glass powder after by sieving is placed in impregnating active 8 hours or so in inorganic acid, and inorganic acid accounts for glass powder gross weight 5% or so of amount, selected inorganic acid is 1.5mol/L nitric acid and 0.8mol/L dichromic acid mixed solutions, the effect of inorganic acid soak It is to make the size generation on glass powder surface swelling, destroys its cross-linked structure between glass fibre;
Nitric acid:Dichromic acid(V/V)=1:2;
(4)It is filtered to remove acid solution(Acid solution is reusable), filter residue is obtained, 15 weight portion LiOH/ are added in 100 weight portion filter residues Al2O3With KOH mixtures, LiOH/ Al2O3It is 1 with the weight ratio of KOH:2,2.5 weight portion stearic acid, 1 weight portion organosilicon disappears Infusion(Foam can be produced during stirring reaction)With 400 parts by weight of cyclohexane solvents, various raw materials are well mixed and are poured into instead Kettle is answered, mixing speed is 2500r/min, at 50 °C, 6h is reacted under conditions of 0.5MPa;
(5)Separation of solid and liquid after 6h, liquid carries out solvent recovery in being directly entered triple effect evaporation tower, after solid dries 2h at 100 °C Directly return kiln and smelt calcining.
Be glass waste silk ESEM comparison diagram after treatment shown in accompanying drawing 2, it is untreated as shown in Figure 2 before glass waste silk Because the parcel of size shows smooth, and after size is divested completely, in glass surface residual fraction size Relic, the rough glass surface of exposing surface after washing can remove most sizes after implementing technique of the invention Remove.
Embodiment 2
The low temperature closed-loop process technique of polyester-type glass fiber waste silk, comprises the following steps:
(1)Polyester-type glass fiber waste silk is cleaned by ultrasonic, supersonic frequency is 90KHz, scavenging period is 10min, is cleaned 3h is dried after 90 °C;
(2)Dried discarded glass cuts into short silk of the length less than 2mm, and air-flow ultramicro grinding is sent under air-flow drive Machine, air velocity is the hypervelocity swirling eddy of more than 1.8MHz, and discharge pressure is 1MPa, and 200 mesh sieve are crossed after crushing;
(3)Discarded glass powder after by sieving be placed in account for glass powder gross weight 10% 10 parts of 0.2-0.8mol/L perchloric acid and 10h is soaked in 20 parts of 2-3mol/L sulfuric acid mixed solutions, makes the size generation on glass powder surface swelling, destroy itself and glass Cross-linked structure between fiber;
(4)It is filtered to remove acid solution(Acid solution is reusable), 20 parts of CsOH, 2 parts of cetyl ammonium bromides are added in 100 parts of filter residues With the mixture of sorbierite(The weight ratio of cetyl ammonium bromide and sorbierite is 4:1), 1.2 parts of organosilicons and polyether antifoam agent Mixture(The weight ratio of organosilicon and polyethers is 3:1)With 200 parts of dichloromethane solvents, poured into after various raw materials are well mixed Reactor, mixing speed is 2500r/min, at 80 DEG C, 2h is reacted under conditions of 0.5MPa;
(5)Separation of solid and liquid after 2h, liquid carries out solvent recovery in being directly entered triple effect evaporation tower, and solid dries 1.5h at 150 DEG C Kiln is directly returned afterwards smelts calcining.
Elementary analysis Comparative result table
Carry out processing the determination of elemental analysis of forward and backward glass waste silk by taking case study on implementation 2 as an example, analyze the data in above table, Draw following conclusion:Untreated glass surface is because the presence of organic type size, and the content of C, H, N is higher.Closed in low temperature After ring PROCESS FOR TREATMENT, the content of C, H, N is rapidly reduced, it was demonstrated that the size on surface is substantially all to be divested.Compared to conventional high-temperature The processing method of calcining, method provided by the present invention has saved energy consumption without high-temperature process, and agents useful for same is recyclable heavy Multiple to utilize, per ton cost can be controlled in less than 500 yuan.
Embodiment 3
The low temperature closed-loop process technique of acrylic ester type glass fiber waste silk, comprises the following steps:
(1)Acrylic ester type glass fiber waste silk is cleaned by ultrasonic, supersonic frequency is 80KHz, scavenging period is 12min, Cleaning dries 3h after 90 °C;
(2)Dried discarded glass cuts into short silk of the length less than 2mm, and air-flow ultramicro grinding is sent under air-flow drive Machine, air velocity is the hypervelocity swirling eddy of more than 1.8MHz, and discharge pressure is 0.5MPa, and 200 mesh sieve are crossed after crushing;
(3)Discarded glass powder after by sieving be placed in account for 10 part of 20% hydrochloric acid of glass powder gross weight 3%, 15% dichromic acid and 8h is soaked in 15% perchloric acid solution(Bichromate solution is 1 with the volume ratio of perchloric acid solution:1), make the leaching on glass powder surface Profit agent generation is swelling, destroys its cross-linked structure between glass fibre;
(4)It is filtered to remove acid solution(Acid solution is reusable), 10 parts of KOH, 4 parts of sorbierites, 1.5 parts of acyls are added in 100 parts of filter residues Amine defoamer(Foam is produced during stirring reaction)With 250 parts of cyclohexane solvents, various raw materials are well mixed and pour into reaction Kettle, mixing speed is 3000r/min, at 60 °C, 4h is reacted under conditions of 1MPa;
(5)Separation of solid and liquid after 4h, liquid carries out solvent recovery in being directly entered triple effect evaporation tower, after solid dries 4h at 100 °C Directly return kiln and smelt calcining.Kiln calcining can be directly returned after dried process and prepares glass fibre, discard glass surface size Clearance can reach more than 98%, the loss late of selected solvent is less than 1 ‰.

Claims (8)

1. the low temperature closed-loop process technique of glass is discarded, including:
(1)The discarded glass of cleaning, dries;
(2)Crush, obtain glass powder;
(3)The treatment of inorganic acid impregnating active;
(4)Catalyst, defoamer, surfactant and solvent are placed in reactor and process;
(5)Dry, calcining prepares glass fibre.
2. the low temperature closed-loop process technique of glass is discarded as claimed in claim 1, it is characterised in that discarded glass includes epoxy Resin type glass, unsaturated polyester type glass, acrylic ester type glass, phenolic resin type glass, polyurethane-type glass etc. are discarded Glass.
3. the low temperature closed-loop process technique of glass is discarded as claimed in claim 1, it is characterised in that using the side being cleaned by ultrasonic To discarded glass cleaning, supersonic frequency is 30~100KHz to method, and scavenging period is 1~15min;Glass waste silk after cleaning is in 80 5~10h is dried at~120 DEG C.
4. the low temperature closed-loop process technique of glass is discarded as claimed in claim 1, it is characterised in that by dried discarded glass Fibre cuts into short silk of the length less than 2mm, sends into air-flow micronizer, and air velocity is the hypervelocity rotary pneumatic of more than 1.5MHZ Stream, discharge pressure is 0.5~1.2MPa.
5. the low temperature closed-loop process technique of glass is discarded as claimed in claim 1, it is characterised in that inorganic acid impregnation process is walked Suddenly specifically, the pH value of pickling bath liquor is 1~5, inorganic acid is hydrochloric acid, sulfuric acid, nitric acid, phosphoric acid, hypochlorous acid, dichromic acid, chlorine high At least one in acid, inorganic acid addition is the 3~10% of glass powder gross weight, and the impregnating active time is 6~10h.
6. the low temperature closed-loop process technique of glass is discarded as claimed in claim 1, it is characterised in that
Catalyst includes Al2O3, KNO3/Al2O3, KOH/Al2O3, NaOH/ Al2O3, LiOH/ Al2O3, CsOH/ Al2O3, NaOH, At least one in KOH, LiOH, CsOH;
Solvent includes at least one in water, lower alcohol, organic alkane, ethers;
Surfactant is stearic acid, neopelex, stearyl dimethyl benzyl ammonium chloride, cetyl bromination At least one in ammonium, sorbierite surfactant;
Defoamer is organic silicon defoamer, polyethers defoamer, silicon and ether grafting class defoamer, defoamer containing amine, imines At least one of class defoamer and amide-type defoamer;
Glass powder after activation:Catalyst:Solvent:Surfactant:The quality parts ratio of defoamer is 20~30:3~8:80~ 100:0.5~1.2:0.1~0.8.
7. the low temperature closed-loop process technique of glass is discarded as claimed in claim 1, it is characterised in that(4)In reaction condition It is as follows:Under the conditions of 50~120 DEG C, pressure is 0.5~1MPa, stirs 4~12h, and stir speed (S.S.) is 1000~3000r/min.
8. the low temperature closed-loop process technique of glass is discarded as claimed in claim 1, it is characterised in that warp(4)Glass after treatment Glass fiber evaporates, and after reclaiming solvent for use, 1h~5h is dried at 100~250 DEG C, and dried glass fibre returns kiln calcining system Standby glass fibre.
CN201710203766.3A 2017-03-30 2017-03-30 The low temperature closed-loop process technique of discarded glass Active CN106927695B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710203766.3A CN106927695B (en) 2017-03-30 2017-03-30 The low temperature closed-loop process technique of discarded glass

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710203766.3A CN106927695B (en) 2017-03-30 2017-03-30 The low temperature closed-loop process technique of discarded glass

Publications (2)

Publication Number Publication Date
CN106927695A true CN106927695A (en) 2017-07-07
CN106927695B CN106927695B (en) 2019-07-19

Family

ID=59425305

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710203766.3A Active CN106927695B (en) 2017-03-30 2017-03-30 The low temperature closed-loop process technique of discarded glass

Country Status (1)

Country Link
CN (1) CN106927695B (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108610852A (en) * 2018-05-02 2018-10-02 济南航晨生物科技有限公司 A method of preparing green environmental friendly coatings using glass waste silk
CN108975680A (en) * 2018-09-18 2018-12-11 重庆国际复合材料股份有限公司 A kind of glass fibre operates on the recovery method of silk
CN110590188A (en) * 2019-08-29 2019-12-20 泰山玻璃纤维邹城有限公司 Processing method of waste glass fiber powder
US20200115263A1 (en) * 2017-07-06 2020-04-16 Hohai University Nanometer photocatalyst-microbe composite multilayer light transmission combination carrier
CN114453388A (en) * 2022-01-27 2022-05-10 四川浩方汇通复合材料有限公司 Glass fiber solid waste silk re-modification utilization treatment production line and treatment process
CN114904889A (en) * 2022-05-24 2022-08-16 五河县维佳复合材料有限公司 Method for preparing high-quality glass fiber powder by recycling glass fiber material

Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB744424A (en) * 1953-08-15 1956-02-08 Fothergill & Harvey Ltd Improvements in the desizing of glass fibres and fabrics
US5895781A (en) * 1997-12-22 1999-04-20 S. C. Johnson & Son, Inc. Cleaning compositions for ceramic and porcelain surfaces and related methods
CN1486948A (en) * 2002-09-30 2004-04-07 张毓强 Production process of glass fiber with waste glass fiber as material
CN1869187A (en) * 2006-06-28 2006-11-29 何北菁 Cleaning agent for waste teletron broken glass and its preparation method
CN102329065A (en) * 2011-06-21 2012-01-25 重庆国际复合材料有限公司 Method for producing glass fiber by using different waste glass fibers and batches
CN102408190A (en) * 2011-08-29 2012-04-11 巨石集团成都有限公司 Method for producing glass fibers by using glass fiber waste silks
CN102489492A (en) * 2011-12-09 2012-06-13 重庆国际复合材料有限公司 Recovery method for glass fiber waste silks
CN102500609A (en) * 2011-10-28 2012-06-20 巨石集团有限公司 Glass fiber waste silk recycling production process
CN102701605A (en) * 2012-06-25 2012-10-03 天津工业大学 Preparation method for alumina/quartz glass composite fiber
CN103787593A (en) * 2014-01-10 2014-05-14 巨石集团有限公司 Preparation method for alkali-resistant fiberglass

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB744424A (en) * 1953-08-15 1956-02-08 Fothergill & Harvey Ltd Improvements in the desizing of glass fibres and fabrics
US5895781A (en) * 1997-12-22 1999-04-20 S. C. Johnson & Son, Inc. Cleaning compositions for ceramic and porcelain surfaces and related methods
CN1486948A (en) * 2002-09-30 2004-04-07 张毓强 Production process of glass fiber with waste glass fiber as material
CN1869187A (en) * 2006-06-28 2006-11-29 何北菁 Cleaning agent for waste teletron broken glass and its preparation method
CN102329065A (en) * 2011-06-21 2012-01-25 重庆国际复合材料有限公司 Method for producing glass fiber by using different waste glass fibers and batches
CN102408190A (en) * 2011-08-29 2012-04-11 巨石集团成都有限公司 Method for producing glass fibers by using glass fiber waste silks
CN102500609A (en) * 2011-10-28 2012-06-20 巨石集团有限公司 Glass fiber waste silk recycling production process
CN102489492A (en) * 2011-12-09 2012-06-13 重庆国际复合材料有限公司 Recovery method for glass fiber waste silks
CN102701605A (en) * 2012-06-25 2012-10-03 天津工业大学 Preparation method for alumina/quartz glass composite fiber
CN103787593A (en) * 2014-01-10 2014-05-14 巨石集团有限公司 Preparation method for alkali-resistant fiberglass

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20200115263A1 (en) * 2017-07-06 2020-04-16 Hohai University Nanometer photocatalyst-microbe composite multilayer light transmission combination carrier
US10889517B2 (en) * 2017-07-06 2021-01-12 Hohai University Nanometer photocatalyst-microbe composite multilayer light transmission combination carrier
CN108610852A (en) * 2018-05-02 2018-10-02 济南航晨生物科技有限公司 A method of preparing green environmental friendly coatings using glass waste silk
CN108975680A (en) * 2018-09-18 2018-12-11 重庆国际复合材料股份有限公司 A kind of glass fibre operates on the recovery method of silk
CN110590188A (en) * 2019-08-29 2019-12-20 泰山玻璃纤维邹城有限公司 Processing method of waste glass fiber powder
CN114453388A (en) * 2022-01-27 2022-05-10 四川浩方汇通复合材料有限公司 Glass fiber solid waste silk re-modification utilization treatment production line and treatment process
CN114904889A (en) * 2022-05-24 2022-08-16 五河县维佳复合材料有限公司 Method for preparing high-quality glass fiber powder by recycling glass fiber material
CN114904889B (en) * 2022-05-24 2023-03-10 五河县维佳复合材料有限公司 Method for preparing high-quality glass fiber powder by recycling glass fiber material

Also Published As

Publication number Publication date
CN106927695B (en) 2019-07-19

Similar Documents

Publication Publication Date Title
CN106927695B (en) The low temperature closed-loop process technique of discarded glass
CN101811695B (en) Method for recovering graphite from electrolytic aluminum waste cathode carbon block
CN104176737B (en) Method for recovering silicon powder from cut mortar waste
CN101817526B (en) Method for recovering polyethylene glycol and silicon carbide from silicon crystal cutting waste liquid
CN103072989B (en) Method for recycling boron carbide in sapphire polishing waste slurry
CN109119711A (en) A method of high-voltage anode material is prepared using waste and old cobalt acid lithium battery
CN102010785A (en) Method for recovering silicon carbide micropowder and wire-cutting fluid from silicon slice wire-cutting processing waste mortar
CN112635867A (en) Method for recovering waste lithium battery graphite material
CN110157916A (en) A kind of method using neodymium iron boron oil base slice greasy filth preparation high-performance anisotropy NdFeB magnetic powder of low cost
CN113651341A (en) Method for synthesizing lithium hexafluorophosphate solution by using fluorine-containing waste residues
CN103072988A (en) Method for recycling boron carbide in sapphire grinding waste slurry
CN107082581A (en) A kind of method of glass fiber waste silk or product normal temperature and pressure repeat glass fiber
CN106283894B (en) A kind of graphene oxide is modified filter paper and preparation method and application
CN113603929A (en) Recovery method of epoxy resin composite material, obtained glass fiber and application thereof
CN103199319B (en) Method for recycling lithium cobalt oxide from waste positive electrode of lithium cobalt oxide battery
CN102390832A (en) Method for treating waste silicon powder produced in trichlorosilane synthesis process
CN110590188B (en) Processing method of waste glass fiber powder
CN109794080A (en) It is a kind of can magnetic recovery composite diatomite demulsifying material preparation method and application
CN104894696A (en) Method for recovering fibers from diaphragmless filter paper edgings
CN107583646A (en) It is a kind of from useless SCR catalyst Green reclaiming Fe2O3/TiO2The method of photochemical catalyst
CN103350996A (en) Method of recycling diamond from liquid resin
CN109796041A (en) Partition separation and recovery utilizes method in a kind of waste and old lead acid accumulator
CN107720734A (en) It is a kind of to prepare the method with fluorescent characteristic graphene quantum dot using waste biomass resource
CN101954675A (en) Method for recovering mortar in wire cutting process
CN102886308A (en) Method for recycling waste rare-earth polishing powder

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
CP03 Change of name, title or address

Address after: 250353 University Road, Changqing District, Ji'nan, Shandong Province, No. 3501

Patentee after: Qilu University of Technology (Shandong Academy of Sciences)

Country or region after: China

Address before: 250353 University Road, Changqing District, Ji'nan, Shandong Province, No. 3501

Patentee before: Qilu University of Technology

Country or region before: China

CP03 Change of name, title or address