CN106057264B - A kind of Spent Radioactive method for treating water of high-efficiency environment friendly - Google Patents

A kind of Spent Radioactive method for treating water of high-efficiency environment friendly Download PDF

Info

Publication number
CN106057264B
CN106057264B CN201610415004.5A CN201610415004A CN106057264B CN 106057264 B CN106057264 B CN 106057264B CN 201610415004 A CN201610415004 A CN 201610415004A CN 106057264 B CN106057264 B CN 106057264B
Authority
CN
China
Prior art keywords
graphene oxide
water
film
environment friendly
efficiency environment
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.)
Expired - Fee Related
Application number
CN201610415004.5A
Other languages
Chinese (zh)
Other versions
CN106057264A (en
Inventor
王文庆
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.)
Liaoning Haihua Energy Equipment Group Co ltd
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to CN201610415004.5A priority Critical patent/CN106057264B/en
Publication of CN106057264A publication Critical patent/CN106057264A/en
Application granted granted Critical
Publication of CN106057264B publication Critical patent/CN106057264B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • GPHYSICS
    • G21NUCLEAR PHYSICS; NUCLEAR ENGINEERING
    • G21FPROTECTION AGAINST X-RADIATION, GAMMA RADIATION, CORPUSCULAR RADIATION OR PARTICLE BOMBARDMENT; TREATING RADIOACTIVELY CONTAMINATED MATERIAL; DECONTAMINATION ARRANGEMENTS THEREFOR
    • G21F9/00Treating radioactively contaminated material; Decontamination arrangements therefor
    • G21F9/04Treating liquids
    • G21F9/06Processing
    • G21F9/12Processing by absorption; by adsorption; by ion-exchange
    • GPHYSICS
    • G21NUCLEAR PHYSICS; NUCLEAR ENGINEERING
    • G21FPROTECTION AGAINST X-RADIATION, GAMMA RADIATION, CORPUSCULAR RADIATION OR PARTICLE BOMBARDMENT; TREATING RADIOACTIVELY CONTAMINATED MATERIAL; DECONTAMINATION ARRANGEMENTS THEREFOR
    • G21F9/00Treating radioactively contaminated material; Decontamination arrangements therefor
    • G21F9/04Treating liquids
    • G21F9/06Processing

Abstract

The invention discloses a kind of Spent Radioactive method for treating water of high-efficiency environment friendly, including pretreatment, UF membrane and post processing, the pretreatment includes the activated carbon filtering carried out successively and ultrafiltration membrance filter, UF membrane is the filtering of graphene oxide group compound film, graphene oxide group compound film is prepared on the flake porous carrier that silane coupler is modified in advance after the compound poly-dopamine of graphene oxide, its film layer two dimension aquaporin is less than 0.45nm, post-process as two-pass reverse osmosis processing, the μ s/cm of water conductivity≤40 handled by two-pass reverse osmosis, reach the emission request of radioactive substance.This method can effectively remove the radioactive substance in waste water, and its stability is good, simple to operate, and cost is low.

Description

A kind of Spent Radioactive method for treating water of high-efficiency environment friendly
Technical field:
The present invention relates to Spent Radioactive water treatment field, a kind of Spent Radioactive water process side of high-efficiency environment friendly is specifically related to Method.
Background technology:
The fast development of China's economy and the continuous exhaustion of fossil energy, turn into the extensive development of nuclear energy and necessarily select Select.After in March, 2011 Japan's generation Fukushima nuclear accident, nuclear safety and nuclear waste transmutation importance are increasingly closed by people Note.With developing rapidly for China's nuclear power industry, to the demand of economic, efficient Radwastes treatment new technology also increasingly Urgently, in addition, application of the radionuclide in military affairs, the energy, industry, agricultural, medical science and other scientific researches increasingly Extensively, quantity of caused radioactive emission, waste liquid and solid waste is also more and more during these, endangers also increasingly Greatly.In radioactivity " three wastes ", the volume of radioactive wastewater and contained radioactivity total amount account for the ratio of radwaste total amount Example is all very big, and therefore, the processing to radioactive wastewater should especially be paid attention to.
Currently used Spent Radioactive water technology mainly includes chemical precipitation method, ion-exchange, absorption method, evaporation Concentration, membrane separation technique, biological treatment etc..Chemical precipitation method process is simple, and expense is relatively low, is given up suitable for salt content is higher Water, but its coefficient of purification is low;Ion-exchange purification efficiency high, absorption range of choice it is wide, suitable for salt content it is low and suspend The poor system of thing, but blockage problem be present, adsorbent reactivation and recovery are difficult easily by high Effects of Salinity in it;Evaporate dense Contracting method coefficient of purification is high, and flexibility is big, technology relative maturity, and securely and reliably, but technological requirement is horizontal high, and operating cost is high, The problems such as corrosion and scaling be present;(4) the easily real large-scale operation of ultrafiltration, suspended particulates and colloid ion are contained suitable for separation Waste water, inoranic membrane has good chemical stability and a radiation resistance, but film vulnerable to pollution, and organic film is easily broken by radiation It is bad;Hyperfiltration energy consumption is low, easy large-scale operation, and suitable for separating inorganic ions waste water, but it is easily contaminated.
Membrane separation technique compared with the treatment technology of routine, has as a kind of emerging Spent Radioactive water technology Lot of advantages:(1) normal-temperature operation, energy consumption are low;(2) take up an area less, it is simple to operate;(3) wide adaptability, for various forms in waste water Pollutant, corresponding membrane process, membrane material, membrane module can be selected to be handled:(4) easily carried out with conventional treatment process It is integrated.Therefore, membrane separation technique has very big potentiality in Spent Radioactive water process.
Chinese patent (200410042589.8) discloses a kind of Spent Radioactive method for treating water, including pretreatment, film point From with post processing three steps;The pretreatment includes the precision safety filtering, activated carbon filtering and milipore filter mistake carried out successively Filter, UF membrane are carried out in nanofiltration membrane component, and post processing is carried out in anion-cation exchange resin processing system, and this method can Effectively to remove the radioactive substance in water, cost is low, easy to operate, but used membrane stability is poor, radionuclide profit The rejection of breath is low.
The content of the invention:
It is an object of the invention to provide a kind of Spent Radioactive method for treating water of high-efficiency environment friendly, this method can be removed effectively Radioactive substance in waste water, the membrane stability employed in wastewater treatment process is good, high to the rejection of radioactive substance.
To achieve the above object, the present invention uses following technical scheme:
A kind of Spent Radioactive method for treating water of high-efficiency environment friendly, comprises the following steps:
(1) pre-process:Radioactive wastewater is filtered off into water removal by activated carbon filtering and ultrafiltration membrance filter, activated carbon successively Middle low molecule radioactive substance, the colloid and all kinds of macromoleculars that ultrafiltration membrance filter is gone in water removal;
(2) UF membrane:Pretreated radioactive wastewater is filtered by graphene oxide group compound film, wherein aoxidizing stone Mertenyl composite membrane is prepared on the flake porous carrier that silane coupler is modified in advance after the compound poly-dopamine of graphene oxide Form, its film layer two dimension aquaporin is less than 0.45nm;
(3) post-process:The post processing is handled for two-pass reverse osmosis, and it is anti-that the concentrated water of second level counter-infiltration returns to the first order In infiltration, the fresh water and the volume ratio of concentrated water that are formed by first-stage reverse osmosis processing are (4-6):1, handled by two-pass reverse osmosis The fresh water of formation and the volume ratio of concentrated water are (8-10):1, the μ s/cm of water conductivity after being handled by two-pass reverse osmosis≤40, reach To the emission request of radioactive substance.
As the preferred of above-mentioned technical proposal, in step (2), the preparation method of the graphene oxide group compound film includes Following steps:
A) flake porous carrier is placed in silane coupler ethanol solution and soaked, after taking-up at 120-150 DEG C at heat 0.5-2h is managed, obtains the flake porous carrier that silane coupler is modified in advance;
B) graphene oxide is placed in water and be dispersed with stirring, add trishydroxymethylaminomethane-hydrochloric acid solution, adjust solution PH to 8-9, ultrasonic 0.5-2h under 500-1000W power, obtain graphene oxide dispersion;
C) Dopamine hydrochloride solution is added into graphene oxide dispersion made from step b), is stirred at 20-80 DEG C 1-6h is reacted, centrifuges 3-5 times, then in 40-60 DEG C of drying, obtains poly-dopamine-graphene oxide compound;
D) poly-dopamine made from step c)-graphene oxide compound and deionized water are mixed evenly, 500W Lower ultrasonic 10-30min, obtains film making solution;
E) film making solution made from step d) is placed in Suction filtration device, modified in advance in silane coupler made from step a) Flake porous carrier surface using vacuum filtration method formed film, then dried in 50 DEG C of baking oven, obtain graphene oxide Group compound film.
As the preferred of above-mentioned technical proposal, in step a), the silane coupler is γ-aminopropyl trimethoxy silicon Alkane, gamma-aminopropyl-triethoxy-silane, γ-(2,3- glycidoxies) propyl trimethoxy silicane, γ-methacryloxypropyl Base propyl trimethoxy silicane, γ-aminopropyltrimethoxysilane, γ-urea propyl-triethoxysilicane, N- (β-aminoethyl)- One or more mixing in gamma-aminopropyl-triethoxy-silane.
As the preferred of above-mentioned technical proposal, in step a), the flake porous carrier is aluminum oxide, silica, oxidation One or more mixing in titanium, makrolon, poly-vinegar acid cellulose, polyacrylonitrile, polytetrafluoroethylene (PTFE), its aperture is 20- 80nm。
As the preferred of above-mentioned technical proposal, in step a), the concentration of the silane coupler ethanol solution is 0.2mM.
As the preferred of above-mentioned technical proposal, in step b), the concentration of the graphene oxide dispersion is 0.1-3mg/ mL。
As the preferred of above-mentioned technical proposal, in step c), the mass ratio of graphene oxide and dopamine is (2-8):1.
As the preferred of above-mentioned technical proposal, in step e), the absolute pressure of the vacuum filtration is 5-10KPa.
The invention has the advantages that:
The present invention uses graphene oxide group compound film in membrane separating process, and it uses dopamine to be answered with graphene oxide Closing, dopamine can effectively adsorb heavy metal ion and radionuclide ion, and graphene oxide has higher hydrophily, And the rejection of radioactive substance is high;This method can effectively remove the radioactive substance in waste water, and in membrane separating process, film is steady It is qualitative good, not vulnerable to pollution.
Embodiment:
In order to be better understood from the present invention, below by embodiment, the present invention is further described, and embodiment is served only for solving The present invention is released, any restriction will not be formed to the present invention.
Embodiment 1
A kind of Spent Radioactive method for treating water of high-efficiency environment friendly, comprises the following steps:
(1) preparation of graphene oxide group compound film:
A) aluminum oxide is placed in the silane coupler ethanol solution that concentration is 0.2mM and soaks 2h, after taking-up at 120 DEG C 0.5h is heat-treated, obtains the aluminum oxide that silane coupler is modified in advance;
B) graphene oxide is placed in water and be dispersed with stirring, add trishydroxymethylaminomethane-hydrochloric acid solution, adjust solution PH to 8-9, ultrasonic 0.5h under 500W power, obtain the graphene oxide dispersion that concentration is 0.1mg/mL;
C) Dopamine hydrochloride solution, the stirring reaction at 20 DEG C are added into graphene oxide dispersion made from step b) 1h, centrifuge 3-5 time, then in 40 DEG C of drying, obtain poly-dopamine-graphene oxide compound, wherein, graphene oxide and more The mass ratio of bar amine is 2:1;
D) poly-dopamine made from step c)-graphene oxide compound and deionized water are mixed evenly, 500W Lower ultrasonic 10min, obtains film making solution;
E) film making solution made from step d) is placed in Suction filtration device, modified in advance in silane coupler made from step a) Oxidation aluminium surface using vacuum filtration method formed film, then dried in 50 DEG C of baking oven, it is compound to obtain graphite oxide alkenyl Film, wherein, the absolute pressure of vacuum filtration is 5KPa;
(2) pre-process:Radioactive wastewater is filtered off into water removal by activated carbon filtering and ultrafiltration membrance filter, activated carbon successively Middle low molecule radioactive substance, the colloid and all kinds of macromoleculars that ultrafiltration membrance filter is gone in water removal;
(3) UF membrane:Pretreated radioactive wastewater is passed through into graphene oxide group compound film mistake made from step (1) Filter, film layer two dimension aquaporin are less than 0.45nm;
(4) post-process:The post processing is handled for two-pass reverse osmosis, and it is anti-that the concentrated water of second level counter-infiltration returns to the first order In infiltration, the fresh water and the volume ratio of concentrated water that are formed by first-stage reverse osmosis processing are 4:1, formed by two-pass reverse osmosis processing Fresh water and concentrated water volume ratio be 8:1, the μ s/cm of water conductivity after being handled by two-pass reverse osmosis≤40, reach radioactivity The emission request of material.
Embodiment 2
A kind of Spent Radioactive method for treating water of high-efficiency environment friendly, comprises the following steps:
(1) preparation of graphene oxide group compound film:
A) polytetrafluoroethylene (PTFE) is placed in the silane coupler ethanol solution that concentration is 0.2mM and soaks 2h, 150 after taking-up 2h is heat-treated at DEG C, obtains the polytetrafluoroethylene (PTFE) that silane coupler is modified in advance;
B) graphene oxide is placed in water and be dispersed with stirring, add trishydroxymethylaminomethane-hydrochloric acid solution, adjust solution PH to 8-9, ultrasonic 2h under 1000W power, obtain the graphene oxide dispersion that concentration is 3mg/mL;
C) Dopamine hydrochloride solution, the stirring reaction at 80 DEG C are added into graphene oxide dispersion made from step b) 6h, centrifuge 3-5 time, then in 60 DEG C of drying, obtain poly-dopamine-graphene oxide compound, wherein, graphene oxide and more The mass ratio of bar amine is 8:1;
D) poly-dopamine made from step c)-graphene oxide compound and deionized water are mixed evenly, 500W Lower ultrasonic 30min, obtains film making solution;
E) film making solution made from step d) is placed in Suction filtration device, modified in advance in silane coupler made from step a) Ptfe surface using vacuum filtration method formed film, then dried in 50 DEG C of baking oven, obtain graphite oxide alkenyl Composite membrane, wherein, the absolute pressure of vacuum filtration is 10KPa;
(2) pre-process:Radioactive wastewater is filtered off into water removal by activated carbon filtering and ultrafiltration membrance filter, activated carbon successively Middle low molecule radioactive substance, the colloid and all kinds of macromoleculars that ultrafiltration membrance filter is gone in water removal;
(3) UF membrane:Pretreated radioactive wastewater is passed through into graphene oxide group compound film mistake made from step (1) Filter, film layer two dimension aquaporin are less than 0.45nm;
(4) post-process:The post processing is handled for two-pass reverse osmosis, and it is anti-that the concentrated water of second level counter-infiltration returns to the first order In infiltration, the fresh water and the volume ratio of concentrated water that are formed by first-stage reverse osmosis processing are 6:1, formed by two-pass reverse osmosis processing Fresh water and concentrated water volume ratio be 10:1, the μ s/cm of water conductivity after being handled by two-pass reverse osmosis≤40, reach radioactivity The emission request of material.
Embodiment 3
A kind of Spent Radioactive method for treating water of high-efficiency environment friendly, comprises the following steps:
(1) preparation of graphene oxide group compound film:
A) silica is placed in the silane coupler ethanol solution that concentration is 0.2mM and soaks 2h, after taking-up at 130 DEG C 0.8h is heat-treated, obtains the silica that silane coupler is modified in advance;
B) graphene oxide is placed in water and be dispersed with stirring, add trishydroxymethylaminomethane-hydrochloric acid solution, adjust solution PH to 8-9, ultrasonic 0.8h under 600W power, obtain the graphene oxide dispersion that concentration is 0.5mg/mL;
C) Dopamine hydrochloride solution, the stirring reaction at 30 DEG C are added into graphene oxide dispersion made from step b) 2h, centrifuge 3-5 time, then in 45 DEG C of drying, obtain poly-dopamine-graphene oxide compound, wherein, graphene oxide and more The mass ratio of bar amine is 4:1;
D) poly-dopamine made from step c)-graphene oxide compound and deionized water are mixed evenly, 500W Lower ultrasonic 15min, obtains film making solution;
E) film making solution made from step d) is placed in Suction filtration device, modified in advance in silane coupler made from step a) Silicon oxide surface using vacuum filtration method formed film, then dried in 50 DEG C of baking oven, it is compound to obtain graphite oxide alkenyl Film, wherein, the absolute pressure of vacuum filtration is 6KPa;
(2) pre-process:Radioactive wastewater is filtered off into water removal by activated carbon filtering and ultrafiltration membrance filter, activated carbon successively Middle low molecule radioactive substance, the colloid and all kinds of macromoleculars that ultrafiltration membrance filter is gone in water removal;
(3) UF membrane:Pretreated radioactive wastewater is passed through into graphene oxide group compound film mistake made from step (1) Filter, film layer two dimension aquaporin are less than 0.45nm;
(4) post-process:The post processing is handled for two-pass reverse osmosis, and it is anti-that the concentrated water of second level counter-infiltration returns to the first order In infiltration, the fresh water and the volume ratio of concentrated water that are formed by first-stage reverse osmosis processing are 5:1, formed by two-pass reverse osmosis processing Fresh water and concentrated water volume ratio be 9:1, the μ s/cm of water conductivity after being handled by two-pass reverse osmosis≤40, reach radioactivity The emission request of material.
Embodiment 4
A kind of Spent Radioactive method for treating water of high-efficiency environment friendly, comprises the following steps:
(1) preparation of graphene oxide group compound film:
A) titanium oxide is placed in the silane coupler ethanol solution that concentration is 0.2mM and soaks 2h, after taking-up at 140 DEG C 1h is heat-treated, obtains the titanium oxide that silane coupler is modified in advance;
B) graphene oxide is placed in water and be dispersed with stirring, add trishydroxymethylaminomethane-hydrochloric acid solution, adjust solution PH to 8-9, ultrasonic 1h under 700W power, obtain the graphene oxide dispersion that concentration is 1mg/mL;
C) Dopamine hydrochloride solution, the stirring reaction at 50 DEG C are added into graphene oxide dispersion made from step b) 3h, centrifuge 3-5 time, then in 50 DEG C of drying, obtain poly-dopamine-graphene oxide compound, wherein, graphene oxide and more The mass ratio of bar amine is 5:1;
D) poly-dopamine made from step c)-graphene oxide compound and deionized water are mixed evenly, 500W Lower ultrasonic 20min, obtains film making solution;
E) film making solution made from step d) is placed in Suction filtration device, modified in advance in silane coupler made from step a) Titania surface using vacuum filtration method formed film, then dried in 50 DEG C of baking oven, it is compound to obtain graphite oxide alkenyl Film, wherein, the absolute pressure of vacuum filtration is 7KPa;
(2) pre-process:Radioactive wastewater is filtered off into water removal by activated carbon filtering and ultrafiltration membrance filter, activated carbon successively Middle low molecule radioactive substance, the colloid and all kinds of macromoleculars that ultrafiltration membrance filter is gone in water removal;
(3) UF membrane:Pretreated radioactive wastewater is passed through into graphene oxide group compound film mistake made from step (1) Filter, film layer two dimension aquaporin are less than 0.45nm;
(4) post-process:The post processing is handled for two-pass reverse osmosis, and it is anti-that the concentrated water of second level counter-infiltration returns to the first order In infiltration, the fresh water and the volume ratio of concentrated water that are formed by first-stage reverse osmosis processing are 4:1, formed by two-pass reverse osmosis processing Fresh water and concentrated water volume ratio be 8:1, the μ s/cm of water conductivity after being handled by two-pass reverse osmosis≤40, reach radioactivity The emission request of material.
Embodiment 5
A kind of Spent Radioactive method for treating water of high-efficiency environment friendly, comprises the following steps:
(1) preparation of graphene oxide group compound film:
A) by poly-vinegar acid cellulose be placed in concentration be 0.2mM silane coupler ethanol solution in soak 2h, after taking-up 1.5h is heat-treated at 145 DEG C, obtains the poly-vinegar acid cellulose that silane coupler is modified in advance;
B) graphene oxide is placed in water and be dispersed with stirring, add trishydroxymethylaminomethane-hydrochloric acid solution, adjust solution PH to 8-9, ultrasonic 1.5h under 800W power, obtain the graphene oxide dispersion that concentration is 2mg/mL;
C) Dopamine hydrochloride solution, the stirring reaction at 70 DEG C are added into graphene oxide dispersion made from step b) 5h, centrifuge 3-5 time, then in 55 DEG C of drying, obtain poly-dopamine-graphene oxide compound, wherein, graphene oxide and more The mass ratio of bar amine is 7:1;
D) poly-dopamine made from step c)-graphene oxide compound and deionized water are mixed evenly, 500W Lower ultrasonic 25min, obtains film making solution;
E) film making solution made from step d) is placed in Suction filtration device, modified in advance in silane coupler made from step a) Poly- surface of cellulose acetate using vacuum filtration method formed film, then dried in 50 DEG C of baking oven, obtain graphene oxide Group compound film, wherein, the absolute pressure of vacuum filtration is 8KPa;
(2) pre-process:Radioactive wastewater is filtered off into water removal by activated carbon filtering and ultrafiltration membrance filter, activated carbon successively Middle low molecule radioactive substance, the colloid and all kinds of macromoleculars that ultrafiltration membrance filter is gone in water removal;
(3) UF membrane:Pretreated radioactive wastewater is passed through into graphene oxide group compound film mistake made from step (1) Filter, film layer two dimension aquaporin are less than 0.45nm;
(4) post-process:The post processing is handled for two-pass reverse osmosis, and it is anti-that the concentrated water of second level counter-infiltration returns to the first order In infiltration, the fresh water and the volume ratio of concentrated water that are formed by first-stage reverse osmosis processing are 6:1, formed by two-pass reverse osmosis processing Fresh water and concentrated water volume ratio be 10:1, the μ s/cm of water conductivity after being handled by two-pass reverse osmosis≤40, reach radioactivity The emission request of material.

Claims (7)

1. the Spent Radioactive method for treating water of a kind of high-efficiency environment friendly, it is characterised in that comprise the following steps:
(1) pre-process:Radioactive wastewater is filtered off low in water removal by activated carbon filtering and ultrafiltration membrance filter, activated carbon successively Molecular radiation material, the colloid and all kinds of macromoleculars that ultrafiltration membrance filter is gone in water removal;
(2) UF membrane:Pretreated radioactive wastewater is filtered by graphene oxide group compound film, wherein graphene oxide Group compound film is prepared on the flake porous carrier that silane coupler is modified in advance after the compound poly-dopamine of graphene oxide , its film layer two dimension aquaporin is less than 0.45nm;Wherein, the preparation method of graphene oxide group compound film comprises the following steps:
A) flake porous carrier is placed in silane coupler ethanol solution and soaked, is heat-treated after taking-up at 120-150 DEG C 0.5-2h, obtain the flake porous carrier that silane coupler is modified in advance;
B) graphene oxide is placed in water and be dispersed with stirring, add trishydroxymethylaminomethane-hydrochloric acid solution, adjust the pH of solution To 8-9, ultrasonic 0.5-2h, obtains graphene oxide dispersion under 500-1000W power;
C) Dopamine hydrochloride solution, the stirring reaction at 20-80 DEG C are added into graphene oxide dispersion made from step b) 1-6h, centrifuge 3-5 times, then in 40-60 DEG C of drying, obtain poly-dopamine-graphene oxide compound;
D) poly-dopamine made from step c)-graphene oxide compound and deionized water are mixed evenly, surpassed under 500W Sound 10-30min, obtains film making solution;
E) film making solution made from step d) is placed in Suction filtration device, in the piece that silane coupler made from step a) is modified in advance Shape porous carrier surface forms film using vacuum filtration method, is then dried in 50 DEG C of baking oven, obtains graphite oxide alkenyl and answer Close film;
(3) post-process:The post processing is handled for two-pass reverse osmosis, and the concentrated water of second level counter-infiltration returns to first order counter-infiltration In, the fresh water and the volume ratio of concentrated water that are formed by first-stage reverse osmosis processing are (4-6):1, formed by two-pass reverse osmosis processing Fresh water and the volume ratio of concentrated water be (8-10):1, the μ s/cm of water conductivity after being handled by two-pass reverse osmosis≤40, reach and put The emission request of penetrating property material.
A kind of 2. Spent Radioactive method for treating water of high-efficiency environment friendly as claimed in claim 1, it is characterised in that in step a), The silane coupler is γ-aminopropyltrimethoxysilane, gamma-aminopropyl-triethoxy-silane, the γ-(oxygen of 2,3- epoxies third Base) propyl trimethoxy silicane, γ-methacryloxypropyl trimethoxy silane, γ-aminopropyltrimethoxysilane, One or more mixing in γ-urea propyl-triethoxysilicane, N- (β-aminoethyl)-gamma-aminopropyl-triethoxy-silane.
A kind of 3. Spent Radioactive method for treating water of high-efficiency environment friendly as claimed in claim 1, it is characterised in that in step a), The flake porous carrier is aluminum oxide, silica, titanium oxide, makrolon, poly-vinegar acid cellulose, polyacrylonitrile, polytetrafluoro One or more mixing in ethene, its aperture is 20-80nm.
A kind of 4. Spent Radioactive method for treating water of high-efficiency environment friendly as claimed in claim 1, it is characterised in that in step a), The concentration of the silane coupler ethanol solution is 0.2mM.
A kind of 5. Spent Radioactive method for treating water of high-efficiency environment friendly as claimed in claim 1, it is characterised in that in step b), The concentration of the graphene oxide dispersion is 0.1-3mg/mL.
A kind of 6. Spent Radioactive method for treating water of high-efficiency environment friendly as claimed in claim 1, it is characterised in that in step c), The mass ratio of graphene oxide and dopamine is (2-8):1.
A kind of 7. Spent Radioactive method for treating water of high-efficiency environment friendly as claimed in claim 1, it is characterised in that in step e), The absolute pressure of the vacuum filtration is 5-10KPa.
CN201610415004.5A 2016-06-14 2016-06-14 A kind of Spent Radioactive method for treating water of high-efficiency environment friendly Expired - Fee Related CN106057264B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610415004.5A CN106057264B (en) 2016-06-14 2016-06-14 A kind of Spent Radioactive method for treating water of high-efficiency environment friendly

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610415004.5A CN106057264B (en) 2016-06-14 2016-06-14 A kind of Spent Radioactive method for treating water of high-efficiency environment friendly

Publications (2)

Publication Number Publication Date
CN106057264A CN106057264A (en) 2016-10-26
CN106057264B true CN106057264B (en) 2018-02-02

Family

ID=57170939

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610415004.5A Expired - Fee Related CN106057264B (en) 2016-06-14 2016-06-14 A kind of Spent Radioactive method for treating water of high-efficiency environment friendly

Country Status (1)

Country Link
CN (1) CN106057264B (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109260962A (en) * 2018-11-20 2019-01-25 南京大学 A kind of method of the composite membrane and its application of the efficient rapid acquiring of heavy metal in complex system

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107665746B (en) * 2016-07-27 2020-01-14 东华理工大学 Device for adsorbing and separating uranium in radioactive wastewater by using graphene oxide dispersion liquid
CN106448791B (en) * 2016-12-12 2018-06-29 河北工业大学 A kind of experimental method using adsorption method for purifying simulated emission waste water
CN109966931A (en) * 2019-04-07 2019-07-05 北京化工大学 A kind of preparation method of graphene oxide/attapulgite/polyvinyl alcohol ceramic matrix composite membrane

Family Cites Families (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP6230243B2 (en) * 2013-03-21 2017-11-15 株式会社キクテック Method and apparatus for removing inorganic fine particles from contaminants containing inorganic fine particles
KR101399365B1 (en) * 2013-08-27 2014-05-27 (주)이엔이 Apparatus for disposal of liquid radioactive waste
CN103903879B (en) * 2014-02-19 2017-02-08 国家纳米科学中心 Porous grapheme/ MnO2 composite film and preparation method and application thereof
CN105321589B (en) * 2014-07-23 2018-03-02 上海一鸣过滤技术有限公司 A kind of method that radioactive wastewater is handled using full embrane method
CN104399090A (en) * 2014-11-12 2015-03-11 深圳先进技术研究院 Poly dopamine-modified reduced graphene oxide and preparation method and application thereof
CN105214512B (en) * 2015-10-29 2018-06-15 中国科学院宁波材料技术与工程研究所 A kind of preparation method and applications of carrier surface graphene oxide membrane

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109260962A (en) * 2018-11-20 2019-01-25 南京大学 A kind of method of the composite membrane and its application of the efficient rapid acquiring of heavy metal in complex system

Also Published As

Publication number Publication date
CN106057264A (en) 2016-10-26

Similar Documents

Publication Publication Date Title
Simons Trace element removal from ash dam waters by nanofiltration and diffusion dialysis
CN106057264B (en) A kind of Spent Radioactive method for treating water of high-efficiency environment friendly
CN105664738B (en) A kind of graphene oxide group compound film for Spent Radioactive water process
Long et al. Removal of iodine from aqueous solution by PVDF/ZIF-8 nanocomposite membranes
Chen et al. Functional PVDF ultrafiltration membrane for Tetrabromobisphenol-A (TBBPA) removal with high water recovery
CN103394295B (en) Hydrophilic PVDF (Polyvinylidene Fluoride) composite ultrafiltration membrane and preparation method thereof
CN110665377B (en) High-flux anti-pollution reverse osmosis membrane and preparation method thereof
Xing et al. MOFs self-assembled molecularly imprinted membranes with photoinduced regeneration ability for long-lasting selective separation
CN107638807A (en) ZIF 8/PVDF milipore filters with catalytic action and preparation method thereof under a kind of normal temperature
CN114042387B (en) Photocatalytic degradation dye wastewater separation multilayer composite membrane and preparation method and application thereof
Ge et al. A novel multi-charged draw solute that removes organic arsenicals from water in a hybrid membrane process
Yang et al. Ultrathin g-C3N4 composite Bi2WO6 embedded in PVDF UF membrane with enhanced permeability, anti-fouling performance and durability for efficient removal of atrazine
CN103480283A (en) Preparation method of hydrophilic ethylene/vinyl alcohol copolymer composite flat plate ultrafiltration membrane
CN105321589A (en) Method for treating radioactive wastewater through whole membrane technology
Dong et al. Selective removal of tungstate anions from aqueous solutions by surface anion‐imprinted ceramic membranes
CN106000127A (en) Carbon-containing seawater desalination film, preparation method and application thereof
CN107545940A (en) The Absorptive complex wave processing method of radioactive wastewater
CN103587003A (en) Resource recycling method of waste polymeric microfiltration/ultrafiltration membrane
CN106492644B (en) It is a kind of based on micro emulsion modified Nano Zero-valent Iron-Carbon Materials precoated shet ultrafiltration membrane process for purifying water
Rahman et al. Application of membrane technology in the treatment of waste liquid containing radioactive materials
Wang et al. Catalytic ceramic membrane integrated with granular activated carbon for efficient removal of organic pollutants
Hu et al. Characterization and application of surface-molecular-imprinted-polymer modified TiO2 nanotubes for removal of perfluorinated chemicals
Lu et al. Bio-synthesis of molecularly imprinted membrane with photo-regeneration availability for selective separation applications
JP2018012082A (en) Membrane separation method of aqueous solution by light irradiation
CN113813928B (en) MOF (Metal organic framework) membrane material for extracting uranium from water, and preparation method and application thereof

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
TA01 Transfer of patent application right

Effective date of registration: 20171214

Address after: 318050, the first seven copies of seven new towns, 5 districts and 104 districts, Luqiao District, Zhejiang, Taizhou

Applicant after: Lin Lirong

Address before: 523000 Guangdong province Dongguan City Songshan Lake high tech Industrial Zone Building 406 industrial development productivity

Applicant before: Dongguan Lianzhou Intellectual Property Operation Management Co.,Ltd.

TA01 Transfer of patent application right
GR01 Patent grant
GR01 Patent grant
TR01 Transfer of patent right

Effective date of registration: 20210210

Address after: 125000 room 610 (Dayushan Economic Development Zone), no.41-1, yingta Road, Lianshan District, Huludao City, Liaoning Province

Patentee after: Liaoning Haihua Energy Equipment Group Co.,Ltd.

Address before: 318050 the first seven, seven, 5, 104, Xinqiao Town, Luqiao District, Taizhou, Zhejiang.

Patentee before: Lin Lirong

TR01 Transfer of patent right
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20180202

Termination date: 20210614

CF01 Termination of patent right due to non-payment of annual fee