CN103230779A - Preparation method for nanometer sphere capable of absorbing heavy metal ions - Google Patents

Preparation method for nanometer sphere capable of absorbing heavy metal ions Download PDF

Info

Publication number
CN103230779A
CN103230779A CN2013101855784A CN201310185578A CN103230779A CN 103230779 A CN103230779 A CN 103230779A CN 2013101855784 A CN2013101855784 A CN 2013101855784A CN 201310185578 A CN201310185578 A CN 201310185578A CN 103230779 A CN103230779 A CN 103230779A
Authority
CN
China
Prior art keywords
heavy metal
preparation
ion
product
carrying
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
CN2013101855784A
Other languages
Chinese (zh)
Other versions
CN103230779B (en
Inventor
严锋
袁超
郭江娜
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.)
Yancheng Youpu Environmental Protection Technology Co Ltd
Original Assignee
Suzhou University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Suzhou University filed Critical Suzhou University
Priority to CN201310185578.4A priority Critical patent/CN103230779B/en
Publication of CN103230779A publication Critical patent/CN103230779A/en
Application granted granted Critical
Publication of CN103230779B publication Critical patent/CN103230779B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Abstract

The invention relates to a preparation method for a nanometer sphere capable of absorbing heavy metal ions. The preparation method comprises the following steps of: (a) adding siloxane ionic liquid and nanometer spheres in a mass proportion of 1:(1-10) and 50-100ml of solvents in a reaction container, carrying out ultrasonic processing for 0.5-1 hour to prepare suspension liquid, carrying out condensation and backflow for 24-48 hours under inert gas protection at 65-90 DEG C, and carrying out centrifuging to obtain rough products; (b) adding the solvents into the rough products obtained in the step (a) again, and repeatedly carrying out ultrasonic dispersion and the centrifuging for 3-5 times to obtain purified products; (c) dispersing the purified products obtained in the step (b) into a water solution with the concentration of 1*10<-5>-0.1mol/L for ion exchange for 24-72 hours, and carrying out the centrifuging to obtain ion-exchanged products; and (d) adding deionized water into the ion-exchanged products obtained in the step (c), repeatedly carrying out the ultrasonic dispersion and the centrifuging for 3-5 times, and drying to obtain final products. The preparation method provided by the invention has the advantages that the process is simple, the operation is convenient, and the yield is high; and the prepared nanometer sphere capable of absorbing the heavy metal ions can be used for recycling the different heavy metal ions and can be repeatedly used.

Description

A kind of preparation method of adsorbable heavy metal ion nanometer bead
Technical field
The present invention relates to nanometer particle process method, particularly a kind of preparation method of adsorbable heavy metal ion nanometer bead.
Background technology
Along with the increase of activity in production in the industry such as mining and metallurgy, machine-building, chemical industry, electronics, instrument, many production processes have all produced heavy metal wastewater thereby (as cadmium, lead, copper, mercury etc.).Heavy metal wastewater thereby is that environmental pollution is the most serious and the mankind are endangered one of maximum industrial wastewater, therefore, how to administer the generally attention that heavy metal wastewater thereby has been subjected to all circles.
At present, have for the effective treating method of removing metal ion: chemical precipitation method, ion-exchange, electrochemical treatments, membrane technology, evaporation coagulation, counter-infiltration and electrodialysis etc.The industrial chemical precipitation method that adopts is handled heavy metal wastewater thereby more, but the chemical precipitation method existence easily causes the water quality sclerosis, and is not thorough to the heavy metal ion processing of low concentration, causes shortcomings such as secondary pollution easily.Ion-exchange-resin process can be transferred to heavy metal ion on the resin, but resin is difficult to separate with heavy metal ion, no matter be all not enough to some extent aspect the recycling of resin or aspect the recovery of precious metal.Absorption method is a kind of method that is commonly used to handle heavy metal wastewater thereby, compares with additive method, and this method technology is simple, easy to operate.Wherein adopt merchandise active carbon is adsorbent more, has stronger adsorption capacity, the heavy metal removing rate height, but need through industry extraction and preparation, cost height.
Complex is by central atom, ligand and extraneous the composition.Part provides lone pair electrons or a plurality of delocalized electrons, and central atom is accepted lone pair electrons or a plurality of delocalized electrons, and the two is in conjunction with forming coordinate bond.Transition metal ions is common central ion, thereby heavy metal ion forms complex, group and heavy metal ion that complex can dissociate the original lone pair electrons of formation under certain condition with group (containing elements such as N, the O) combination that contains lone pair electrons easily.This special nature is simple for seeking a kind of making, and adsorption activity height, the heavy metal ion adsorbing material that can reuse provide may.
Summary of the invention
The present invention seeks to provide in order to overcome the deficiencies in the prior art a kind of preparation method who utilizes coordinate bond Adsorption of Heavy Metal Ions nanometer bead.
For solving above technical problem, a kind of technical scheme that the present invention takes is: a kind of preparation method of adsorbable heavy metal ion nanometer bead may further comprise the steps:
(a), in reaction vessel, press mass ratio 1:1~10 and add siloxanes ionic liquid, nanometer bead, 50~500ml solvent, ultrasonic 0.5~1h is configured to suspension, and under 65-90 ℃, inert gas shielding condensing reflux 24-48 hour, centrifugal crude product;
(b), in step (a) crude product, add solvent, ultrasonic dispersion, centrifugal again, repeat the product that to purify for 3~5 times;
(c), the product of purifying in the step (b) being dispersed in concentration is 1 * 10 -5~0.1mol/L's
Figure BDA00003212477700021
Carry out ion-exchange 24~72 hours in the aqueous solution, the centrifugal product that gets ion-exchange;
(d), in the product of step (c) ion-exchange, add deionized water, ultrasonic dispersion, centrifugal, repeat 3~5 times dry end product.
The structural formula of wherein said siloxanes ionic liquid is
Figure BDA00003212477700022
X is selected from a kind of among Cl, I, the Br in the formula, and n and m are separate to be 2 to 5 integer, and R is CH 3, CH 3CH 2, CH 3CH 2CH 2, CH 3CH 2CH 2CH 2In a kind of.
Optimally, described nanometer bead is a kind of in silica, titanium dioxide, zinc oxide, the aluminium oxide, and its particle diameter is 50~200nm.
Optimally, described solvent is a kind of in carrene, the chloroform.
Because technique scheme is used, the present invention compared with prior art has following advantage:
1, this procedure is simple, easy to operate and productive rate is high;
2, the adsorbable heavy metal ion nanometer bead that utilizes this method to prepare can be realized the recovery to different heavy metal ion, and can reuse.
The specific embodiment
Below be specific embodiments of the invention, technical scheme of the present invention is further described, but the present invention is not limited to these embodiment.
Embodiment 1
This example provides a kind of preparation method of adsorbable heavy metal ion nanometer bead, and its concrete steps are as follows:
(a), add 0.1g at reaction vessel
Figure BDA00003212477700023
The nano silicon bead of 1g50nm, the 50ml solvent, ultrasonic 0.5h is configured to suspension, and condensing reflux is 48 hours under 65 ℃, inert gas shielding, centrifugal crude product;
(b), in step (a) crude product, add solvent, ultrasonic dispersion, centrifugal again, repeat the product that to purify for 3 times;
(c), the product of purifying in the step (b) being dispersed in concentration is 1 * 10 -5Mol/L's
Figure BDA00003212477700031
Carry out ion-exchange 72 hours in the aqueous solution, the centrifugal product that gets ion-exchange;
(d), in the product of step (c) ion-exchange, add deionized water, ultrasonic dispersion, centrifugal, repeat 3 times dry end product.
Embodiment 1
This example provides a kind of preparation method of adsorbable heavy metal ion nanometer bead, and its concrete steps are as follows:
(a), add 1g at reaction vessel
Figure BDA00003212477700032
The nano silicon bead of 1g500nm, the 500ml solvent, ultrasonic 1h is configured to suspension, and condensing reflux is 24 hours under 90 ℃, inert gas shielding, centrifugal crude product;
(b), in step (a) crude product, add solvent, ultrasonic dispersion, centrifugal again, repeat the product that to purify for 5 times;
(c), the product of purifying in the step (b) being dispersed in concentration is 0.1mol/L's
Figure BDA00003212477700033
Carry out ion-exchange 24 hours in the aqueous solution, the centrifugal product that gets ion-exchange;
(d), in the product of step (c) ion-exchange, add deionized water, ultrasonic dispersion, centrifugal, repeat 5 times dry end product.
Above-described embodiment only is explanation technical conceive of the present invention and characteristics, and its purpose is to allow the personage who is familiar with this technology can understand content of the present invention and enforcement according to this, can not limit protection scope of the present invention with this.All equivalences that spirit essence is done according to the present invention change or modify, and all should be encompassed within protection scope of the present invention.

Claims (3)

1. the preparation method of an adsorbable heavy metal ion nanometer bead is characterized in that: may further comprise the steps:
(a), in reaction vessel, press mass ratio 1:1~10 and add siloxanes ionic liquid, nanometer bead, 50~500ml solvent, ultrasonic 0.5~1h is configured to suspension, and under 65-90 ℃, inert gas shielding condensing reflux 24-48 hour, centrifugal crude product;
(b), in step (a) crude product, add solvent, ultrasonic dispersion, centrifugal again, repeat the product that to purify for 3~5 times;
(c), the product of purifying in the step (b) being dispersed in concentration is 1 * 10 -5~0.1mol/L's
Figure FDA00003212477600011
Carry out ion-exchange 24~72 hours in the aqueous solution, the centrifugal product that gets ion-exchange;
(d), in the product of step (c) ion-exchange, add deionized water, ultrasonic dispersion, centrifugal, repeat 3~5 times dry end product.
The structural formula of wherein said siloxanes ionic liquid is
Figure FDA00003212477600012
X is selected from a kind of among Cl, I, the Br in the formula, and n and m are separate to be 2 to 5 integer, and R is CH 3, CH 3CH 2, CH 3CH 2CH 2, CH 3CH 2CH 2CH 2In a kind of.
2. the preparation method of adsorbable heavy metal ion nanometer bead according to claim 1 is characterized in that: described nanometer bead is a kind of in silica, titanium dioxide, zinc oxide, the aluminium oxide, and its particle diameter is 50~200nm.
3. the preparation method of adsorbable heavy metal ion nanometer bead according to claim 1 and 2 is characterized in that: described solvent is a kind of in carrene, the chloroform.
CN201310185578.4A 2013-05-20 2013-05-20 Preparation method for nanometer sphere capable of absorbing heavy metal ions Active CN103230779B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201310185578.4A CN103230779B (en) 2013-05-20 2013-05-20 Preparation method for nanometer sphere capable of absorbing heavy metal ions

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201310185578.4A CN103230779B (en) 2013-05-20 2013-05-20 Preparation method for nanometer sphere capable of absorbing heavy metal ions

Publications (2)

Publication Number Publication Date
CN103230779A true CN103230779A (en) 2013-08-07
CN103230779B CN103230779B (en) 2014-10-08

Family

ID=48878887

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201310185578.4A Active CN103230779B (en) 2013-05-20 2013-05-20 Preparation method for nanometer sphere capable of absorbing heavy metal ions

Country Status (1)

Country Link
CN (1) CN103230779B (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107417913A (en) * 2017-08-22 2017-12-01 广东工业大学 A kind of method of heavy metal in organic microporous polymer of nanometer and absorption drinking water

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6544419B1 (en) * 1996-10-31 2003-04-08 University Of Kentucky Research Foundation Method of preparing a composite polymer and silica-based membrane
CN101612597A (en) * 2009-07-27 2009-12-30 中国科学院长春应用化学研究所 The organic-inorganic composite anion exchange resin and the method for making that are used for adsorbing hexavalent chromium ions
CN101785991A (en) * 2009-12-12 2010-07-28 鲁东大学 Preparation method of amino bonded silica gel glycerol adsorbent and prepared product thereof
US20110026024A1 (en) * 2009-07-30 2011-02-03 Industry-University Cooperation Foundation Sogang University Method and apparatus for detecting metal ions, probe used for the same and preparation method thereof

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6544419B1 (en) * 1996-10-31 2003-04-08 University Of Kentucky Research Foundation Method of preparing a composite polymer and silica-based membrane
CN101612597A (en) * 2009-07-27 2009-12-30 中国科学院长春应用化学研究所 The organic-inorganic composite anion exchange resin and the method for making that are used for adsorbing hexavalent chromium ions
US20110026024A1 (en) * 2009-07-30 2011-02-03 Industry-University Cooperation Foundation Sogang University Method and apparatus for detecting metal ions, probe used for the same and preparation method thereof
CN101785991A (en) * 2009-12-12 2010-07-28 鲁东大学 Preparation method of amino bonded silica gel glycerol adsorbent and prepared product thereof

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
XIAOJIAN CHEN, ET AL: "Ionic liquid-tethered nanoparticle/poly(ionic liquid) electrolytes for quasi-solid-state dye-sensitized solar cells", 《JOURNAL OF POWER SOURCES》 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107417913A (en) * 2017-08-22 2017-12-01 广东工业大学 A kind of method of heavy metal in organic microporous polymer of nanometer and absorption drinking water
CN107417913B (en) * 2017-08-22 2020-04-14 广东工业大学 Nano organic microporous polymer and method for adsorbing heavy metals in drinking water

Also Published As

Publication number Publication date
CN103230779B (en) 2014-10-08

Similar Documents

Publication Publication Date Title
CN105384195B (en) Method for recovering rhenium from molybdenum smelting waste acid
CN105731624B (en) A method of utilizing heterogeneous Fenton-like reaction catalytic oxidation treatment reverse osmosis concentrated water
CN108722365B (en) Heavy metal ion adsorption material and preparation method thereof
TW201516156A (en) Method for recycling vanadium and tungsten from waste selective catalytic reduction catalyst
CN103480347A (en) Preparation method of composite flat membrane for adsorbing heavy metal ions and product thereof
CN109706315B (en) Method for adsorbing noble metal complex ions in thiosulfate leaching solution by using molybdenum disulfide
CN112897627A (en) Method for removing heavy metal wastewater
CN104263928B (en) A kind of method of solvent extraction and separation nickel cobalt under super gravity field
CN114870818A (en) Method for adsorbing and separating gold, platinum and palladium by utilizing polyion liquid gel adsorbent
Zuo et al. Fe3O4@ Mesoporous-SiO2@ Chitosan@ Polyaniline core–shell nanoparticles as recyclable adsorbents and reductants for hexavalent chromium
CN104016434A (en) Method for purifying sewage containing heavy metal by utilizing calcium metasilicate and recycling heavy metal
CN108993396A (en) A kind of super-hydrophobic high dispersion nanometer oxide zinc-charcoal compound adsorbent and its preparation method and application
CN104043396A (en) Preparation method and application of magnetic aminated graphene oxide
CN113000023A (en) Graphene oxide modified activated carbon, preparation method thereof and water treatment method
CN104084177A (en) Magnetic chitosan nanofiber copper ion absorbing agent, as well as preparation method and application thereof
Tripathi et al. Removal of U (VI) from aqueous solution by adsorption onto synthesized silica and zinc silicate nanotubes: equilibrium and kinetic aspects with application to real samples
CN103230779B (en) Preparation method for nanometer sphere capable of absorbing heavy metal ions
CN103831081A (en) Adsorbent for processing heavy metal wastewater and heavy metal wastewater processing method
CN111995020B (en) Preparation method of polymeric magnesium aluminum cerium chloride coagulant
CN110560005B (en) Chitosan ionic gel and preparation method and application thereof
CN106268651B (en) Nano SiO 2 particle and its preparation method and application for adsorbing separation platinum
CN106669640B (en) Polyaniline modified bentonite nanoparticle adsorbing material and preparation method thereof
CN108201881B (en) Modified resin material and preparation method and application thereof
CN110846510A (en) Method for efficiently and selectively adsorbing and recovering rhenium and mercury from copper smelting multi-element mixed waste acid
CN113600150B (en) Method for preparing magnetic super-crosslinked polymer from vacuum residue

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
C41 Transfer of patent application or patent right or utility model
TR01 Transfer of patent right

Effective date of registration: 20151013

Address after: 224300 crossing economic zone of Haihe Town, Sheyang County, Jiangsu, Yancheng City

Patentee after: YANCHENG YOUPU ENVIRONMENTAL PROTECTION TECHNOLOGY CO., LTD.

Address before: 215123 Suzhou Industrial Park, Jiangsu Road, No. 199

Patentee before: Soochow University