CN103387237A - Method for recycling optical fiber wastes - Google Patents

Method for recycling optical fiber wastes Download PDF

Info

Publication number
CN103387237A
CN103387237A CN201210142853XA CN201210142853A CN103387237A CN 103387237 A CN103387237 A CN 103387237A CN 201210142853X A CN201210142853X A CN 201210142853XA CN 201210142853 A CN201210142853 A CN 201210142853A CN 103387237 A CN103387237 A CN 103387237A
Authority
CN
China
Prior art keywords
optical fiber
powder
resource recovery
fiber waste
obtains
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.)
Pending
Application number
CN201210142853XA
Other languages
Chinese (zh)
Inventor
许开华
闫梨
张翔
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.)
Jingmen GEM New Material Co Ltd
Shenzhen Gem High Tech Co Ltd
Original Assignee
Jingmen GEM New Material Co Ltd
Shenzhen Gem High Tech Co Ltd
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 Jingmen GEM New Material Co Ltd, Shenzhen Gem High Tech Co Ltd filed Critical Jingmen GEM New Material Co Ltd
Priority to CN201210142853XA priority Critical patent/CN103387237A/en
Publication of CN103387237A publication Critical patent/CN103387237A/en
Pending legal-status Critical Current

Links

Landscapes

  • Processing Of Solid Wastes (AREA)

Abstract

The invention relates to the treatment of electronic waste materials, and particularly relates to a method for recycling optical fiber wastes. The scheme of the method for recycling the optical fiber wastes includes the following steps: (1) crushing the optical fiber wastes into optical fiber powder; (2) cleaning the optical fiber powder and drying; (3) mixing the optical fiber powder and carbon powder evenly; (4) reacting mixed powder in chlorine gas flow conditions at the temperature of 980-1200 DEG C for 1-4 h; and (5) condensing a mixed gas obtained by the reaction, and then obtaining silicon tetrachloride and germanium tetrachloride through fractional distillation of a liquid obtained by the condensation. The method for recycling the optical fiber wastes has the features of short technological process, high product purity, environmental friendliness and the like.

Description

A kind of method of optical fiber waste resource recovery
Technical field
The present invention relates to the processing to the electronics waste and scrap, be specifically related to a kind of method of optical fiber waste resource recovery.
Background technology
Development along with information technology and optic fibre manufacturing technology, whole world optical fiber demand is just with annual 10% speed increase, optical fiber is popularized on a large scale in global information communication, when giving a large amount of high transfer rates of the mankind, annual a large amount of optical fiber waste material to the environment band huge negative impact.At present the resource utilization of optical fiber waste material mainly concentrates on the germanium that extracts wherein, and the technique of using has: 1. hydrofluoric acid lixiviation process, the method adopts the main substance SiO of hydrofluoric acid dissolution optical fiber waste material 2Produce H -2SiF 6, GeO wherein 2Generate H with HF -2GeF 6Enter solution, adopt the heavy germanium of tannic acid after neutralization, carry out finally chlorinated distillation and obtain thick GeCl 4, the shortcoming of the method is that HF is large to equipment corrosion, equipment cost is large; 2. high-temperature roasting after alkali fusion, the method mix with alkali and optical fiber waste material, make SiO 2Change Na into 2SiO 4Destroy SiO 2, to the parcel of germanium, make simultaneously GeO 2Be converted into germanate, then through chlorinated distillation, obtain thick GeCl 4, the shortcoming of the method is to need to consume a large amount of alkali and acid.Above two kinds of techniques, due to himself shortcoming, make it outside obtaining the germanium of high added value, and are also quite serious on the impact of environment.
Summary of the invention
The invention provides a kind of method of optical fiber waste resource recovery, is a kind of novel process of optical fiber comprehensive utilization of waste material, and this technique has the characteristics such as technical process is short, products obtained therefrom purity is high, environmental friendliness.
The method of a kind of optical fiber waste resource recovery of the present invention, its scheme comprises the following steps:
(1) the optical fiber waste material is made the fine powder of 80~200 sight through fragmentation;
(2) clean the optical fiber powder, and dry to constant weight under 100~200 ℃;
(3) the optical fiber powder is mixed with 80~200 purpose carbon dusts, the mass ratio of optical fiber powder and carbon dust is 1:0.1~0.8;
(4) with mixed powder under the cl gas flow condition of 180~300Nl/h, react 1~4h at 980~1200 ℃ of temperature;
(5) Mixed Gas Condensation to 20 that reaction is obtained~40 ℃, and then the liquid fractionation that condensation is obtained, 60~75 ℃ of collections obtain silicon tetrachloride, and 85~95 ℃ of collections obtain germanium tetrachloride.
Preferably,
In step (1), optical fiber is crushed to 120~150 order powder;
Step (2) washed with de-ionized water optical fiber powder, and dry to constant weight under 150~180 ℃;
The mass ratio of step (3) optical fiber powder and carbon dust is 1:0.5;
Step (4) is heated to 1050~1100 ℃;
Cardinal principle of the present invention is, obtain the powder of certain particle size after the fragmentation of optical fiber waste material, adopt the carbon thermal chlorination to obtain silicon tetrachloride and germanium tetrachloride mixed gas, then through fractionation, silicon tetrachloride is separated with germanium tetrachloride, silicon tetrachloride directly reclaims, and obtains germanium dioxide after the germanium tetrachloride hydrolysis.
SiO 2+2C+2Cl 2→SiCl 4+2CO
GeO 2+2C+2Cl 2→GeCl 4+2CO
The method of optical fiber waste resource recovery of the present invention has the characteristics such as technical process is short, products obtained therefrom purity is high, environmental friendliness.
Embodiment
The present invention is further illustrated below in conjunction with specific embodiment, but protection scope of the present invention is not limited to these embodiment.
Embodiment one
The method of optical fiber waste resource recovery, concrete steps are as follows:
(1) the optical fiber waste material makes the fine powder of 120 sight through fragmentation;
(2) dry to constant weight with washed with de-ionized water optical fiber powder and under 150 ℃;
(3) the optical fiber powder mixes with 150 purpose carbon dusts, and the mass ratio of optical fiber powder and carbon dust is 1:0.5;
(4) mixed powder, as in silica tube, passes into the cl gas flow (nitrogen dilution) of 240Nl/h, is heated to 1050 ℃, reaction 2h;
(5) reacting the mixed gas that obtains is transported in condenser and is condensed to 30 ℃ with nitrogen;
(6) liquid that obtains fractionation again, collect the silicon tetrachloride cut under 70 ℃, collect the germanium tetrachloride cut under 90 ℃;
The silicon tetrachloride purity that obtains is 99%, directly as production marketing;
Obtain purity after the hydrolysis of the germanium tetrachloride that obtains and be the germanium dioxide more than 99%.
Embodiment two
The method of optical fiber waste resource recovery, concrete steps are as follows:
(1) the optical fiber waste material makes the fine powder of 150 sight through fragmentation;
(2) dry to constant weight with washed with de-ionized water optical fiber powder and under 180 ℃;
(3) the optical fiber powder mixes with 150 purpose carbon dusts, and the mass ratio of optical fiber powder and carbon dust is 1:0.1;
(4) mixed powder, as in silica tube, passes into the cl gas flow (nitrogen dilution) of 180Nl/h, is heated to 980 ℃, reaction 4h;
(5) reacting the mixed gas that obtains is transported in condenser and is condensed to 30 ℃ with nitrogen;
(6) liquid that obtains fractionation again, collect the silicon tetrachloride cut under 68 ℃, collect the germanium tetrachloride cut under 85 ℃;
The silicon tetrachloride purity that obtains is 98.5%, directly as production marketing;
Obtain purity after the hydrolysis of the germanium tetrachloride that obtains and be the germanium dioxide more than 99%.
Embodiment three
The method of optical fiber waste resource recovery, concrete steps are as follows:
(1) the optical fiber waste material makes the fine powder of 130 sight through fragmentation;
(2) dry to constant weight with washed with de-ionized water optical fiber powder and under 100 ℃;
(3) the optical fiber powder mixes with 130 purpose carbon dusts, and the mass ratio of optical fiber powder and carbon dust is 1:0.8;
(4) mixed powder, as in silica tube, passes into the cl gas flow (nitrogen dilution) of 300Nl/h, is heated to 1200 ℃, reaction 2h;
(5) reacting the mixed gas that obtains is transported in condenser and is condensed to 40 ℃ with nitrogen;
(6) liquid that obtains fractionation again, collect the silicon tetrachloride cut under 75 ℃, collect the germanium tetrachloride cut under 90 ℃;
The silicon tetrachloride purity that obtains is 98%, directly as production marketing;
Obtain purity after the hydrolysis of the germanium tetrachloride that obtains and be the germanium dioxide more than 99%.
Embodiment four
The method of optical fiber waste resource recovery, concrete steps are as follows:
(1) the optical fiber waste material makes the fine powder of 80 sight through fragmentation;
(2) dry to constant weight with washed with de-ionized water optical fiber powder and under 200 ℃;
(3) the optical fiber powder mixes with 200 purpose carbon dusts, and the mass ratio of optical fiber powder and carbon dust is 1:0.4;
(4) mixed powder, as in silica tube, passes into the cl gas flow (nitrogen dilution) of 220Nl/h, is heated to 1100 ℃, reaction 3h;
(5) reacting the mixed gas that obtains is transported in condenser and is condensed to 35 ℃ with nitrogen;
(6) liquid that obtains fractionation again, collect the silicon tetrachloride cut under 70 ℃, collect the germanium tetrachloride cut under 95 ℃;
The silicon tetrachloride purity that obtains is 99%, directly as production marketing;
Obtain purity after the hydrolysis of the germanium tetrachloride that obtains and be the germanium dioxide more than 99%.
Embodiment five
The method of optical fiber waste resource recovery, concrete steps are as follows:
(1) the optical fiber waste material makes the fine powder of 200 sight through fragmentation;
(2) dry to constant weight with washed with de-ionized water optical fiber powder and under 160 ℃;
(3) the optical fiber powder mixes with 80-200 purpose carbon dust, and the mass ratio of optical fiber powder and carbon dust is 1:0.7;
(4) mixed powder, as in silica tube, passes into the cl gas flow (nitrogen dilution) of 200Nl/h, is heated to 1070 ℃, reaction 2.5h;
(5) reacting the mixed gas that obtains is transported in condenser and is condensed to 25 ℃ with nitrogen;
(6) liquid that obtains fractionation again, collect the silicon tetrachloride cut under 75 ℃, collect the germanium tetrachloride cut under 95 ℃;
The silicon tetrachloride purity that obtains is 97.5%, directly as production marketing;
Obtain purity after the hydrolysis of the germanium tetrachloride that obtains and be the germanium dioxide more than 99%.
Embodiment six
The method of optical fiber waste resource recovery, concrete steps are as follows:
(1) the optical fiber waste material makes the fine powder of 140 sight through fragmentation;
(2) dry to constant weight with washed with de-ionized water optical fiber powder and under 180 ℃;
(3) the optical fiber powder mixes with 140 purpose carbon dusts, and the mass ratio of optical fiber powder and carbon dust is 1:0.2;
(4) mixed powder, as in silica tube, passes into the cl gas flow (nitrogen dilution) of 280Nl/h, is heated to 1180 ℃, reacts 1.5 hours;
(5) reacting the mixed gas that obtains is transported in condenser and is condensed to 20 ℃ with nitrogen;
(6) liquid that obtains fractionation again, collect the silicon tetrachloride cut under 75 ℃, collect the germanium tetrachloride cut under 85 ℃;
The silicon tetrachloride purity that obtains is 97%, directly as production marketing;
Obtain purity after the hydrolysis of the germanium tetrachloride that obtains and be the germanium dioxide more than 99%.
Above-described embodiment is the better embodiment of the present invention; but embodiments of the present invention are not restricted to the described embodiments; other any do not deviate from change, the modification done under spirit of the present invention and principle, substitutes, combination, simplify; all should be the substitute mode of equivalence, within being included in protection scope of the present invention.

Claims (5)

1. the method for an optical fiber waste resource recovery, is characterized in that, comprises the following steps:
(1) the optical fiber waste material is made the fine powder of 80~200 sight through fragmentation;
(2) clean the optical fiber powder, and dry to constant weight under 100~200 ℃;
(3) the optical fiber powder is mixed with 80~200 purpose carbon dusts, the mass ratio of optical fiber powder and carbon dust is 1:0.1~0.8;
(4) with mixed powder under the cl gas flow condition of 180~300Nl/h, react 1~4h at 980~1200 ℃ of temperature;
(5) Mixed Gas Condensation that reaction is obtained, and then the liquid fractionation that condensation obtains is obtained silicon tetrachloride and germanium tetrachloride.
2. the method for optical fiber waste resource recovery according to claim 1, is characterized in that, in step (1), optical fiber is crushed to 120~150 order powder.
3. the method for optical fiber waste resource recovery according to claim 1, is characterized in that, step (2) washed with de-ionized water optical fiber powder, and dry to constant weight under 150~180 ℃.
4. the method for optical fiber waste resource recovery according to claim 1, is characterized in that, the mass ratio of step (3) optical fiber powder and carbon dust is 1:0.5.
5. the method for optical fiber waste resource recovery according to claim 1, is characterized in that, step (4) is heated to 1050~1100 ℃.
CN201210142853XA 2012-05-10 2012-05-10 Method for recycling optical fiber wastes Pending CN103387237A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201210142853XA CN103387237A (en) 2012-05-10 2012-05-10 Method for recycling optical fiber wastes

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201210142853XA CN103387237A (en) 2012-05-10 2012-05-10 Method for recycling optical fiber wastes

Publications (1)

Publication Number Publication Date
CN103387237A true CN103387237A (en) 2013-11-13

Family

ID=49531672

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201210142853XA Pending CN103387237A (en) 2012-05-10 2012-05-10 Method for recycling optical fiber wastes

Country Status (1)

Country Link
CN (1) CN103387237A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110079686A (en) * 2018-11-20 2019-08-02 云南驰宏国际锗业有限公司 A kind of germanium scrap metal processing method

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1597533A (en) * 2004-07-27 2005-03-23 南京大学 Production technology of optical fiber grade high purity ger manium tetrachloride
CN1842491A (en) * 2004-08-04 2006-10-04 德古萨公司 Method and device for purifying silicon tetrachloride or germanium tetrachloride containing hydride
CN101925537A (en) * 2007-12-05 2010-12-22 国家科学研究学院 From optical fiber or glass slag, reclaim GeCl 4And/or SiCl 4Method and by being rich in SiO 2Material make SiCl 4Method

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1597533A (en) * 2004-07-27 2005-03-23 南京大学 Production technology of optical fiber grade high purity ger manium tetrachloride
CN1842491A (en) * 2004-08-04 2006-10-04 德古萨公司 Method and device for purifying silicon tetrachloride or germanium tetrachloride containing hydride
CN101925537A (en) * 2007-12-05 2010-12-22 国家科学研究学院 From optical fiber or glass slag, reclaim GeCl 4And/or SiCl 4Method and by being rich in SiO 2Material make SiCl 4Method

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110079686A (en) * 2018-11-20 2019-08-02 云南驰宏国际锗业有限公司 A kind of germanium scrap metal processing method

Similar Documents

Publication Publication Date Title
CN103101914B (en) Intermittent operation method and device for recovery and purification of hexachlorodisilane from chlorosilane residual liquid
CN103738968B (en) The method of recycle fluorochemical in the process preparing silicon-containing compound
CN102642839B (en) Processing process of industrial grade silicon tetrachloride
AU2008331380B2 (en) GeCl4 and/or SiCI4 recovery process from optical fibers or glassy residues and process for producing SiCI4 from SiO2 rich materials
CN102951618A (en) Method for recycling germanium, gallium, indium and selenium in waste diode
CN103420383A (en) Method for preparing fumed silica and anhydrous hydrofluoric acid by utilizing phosphatic fertilizer by-product fluosilicate as raw material
CN102502502A (en) Method for preparing hydrogen fluoride gas from 98% sulphuric acid
CN113651341A (en) Method for synthesizing lithium hexafluorophosphate solution by using fluorine-containing waste residues
CN102001666B (en) Method for producing high-purity silicon tetrafluoride in wet processing of phosphate ore
CN102952951A (en) Method for extracting tantalum and niobium and producing potassium fluosilicate from tungsten smelting slag
CN107265463B (en) The method that calcium fluoride containing waste material prepares fluosilicic acid
CN103708472A (en) Method for preparing SiO2 powder by using zircon sand
CN102701215A (en) Method for preparing silicon tetrafluoride co-production with calcium fluoride by using fluosilicic acid and calcium carbide dust
CN103387237A (en) Method for recycling optical fiber wastes
CN108928825A (en) The method of silica and ammonium fluosilicate is separated and recovered from fluorine-containing dust
CN101691217A (en) Method for preparing white carbon black and simultaneously recycling silicon carbide from waste mortar for wire cutting
CN106621757B (en) Chlorosilane analysis waste gas recovery treatment device and treatment method
CN102001691A (en) Process for producing potassium nitrate by decomposing potassium feldspar at low temperature through fluorine-contained acid
CN102134078A (en) Method for closed-loop production of silicon tetrafluoride by utilizing sulfuric acid and quartz sand
CN102275877A (en) Method for producing anhydrous hydrogen fluoride and silicon tetrafluoride by utilizing fluosilicic acid
CN102557096B (en) Circulating preparation method for producing simple substance boron by using potassium fluoborate as intermediate material and synchronously producing elpasolite
CN108910887A (en) A kind of monocrystalline silicon cuts the recovery and treatment method of slag and cutting waste liquor
CN103193236B (en) Method of preparing silica by using diatomite
CN103708533B (en) One prepares nanometer Ga 2o 3the method of powder
CN114606401A (en) Chlorine-free dry method germanium recovery method

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C12 Rejection of a patent application after its publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20131113