CN115430294A - Roll type nanofiltration membrane element capable of efficiently removing trace heavy metals - Google Patents

Roll type nanofiltration membrane element capable of efficiently removing trace heavy metals Download PDF

Info

Publication number
CN115430294A
CN115430294A CN202210928143.3A CN202210928143A CN115430294A CN 115430294 A CN115430294 A CN 115430294A CN 202210928143 A CN202210928143 A CN 202210928143A CN 115430294 A CN115430294 A CN 115430294A
Authority
CN
China
Prior art keywords
woven fabric
acrylic acid
water
nanofiltration membrane
fabric film
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
CN202210928143.3A
Other languages
Chinese (zh)
Other versions
CN115430294B (en
Inventor
邵艳丽
毕春莹
刘泽宇
陈承
林春儿
刘红星
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Ningbo Fotile Kitchen Ware Co Ltd
Original Assignee
Ningbo Fotile Kitchen Ware 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 Ningbo Fotile Kitchen Ware Co Ltd filed Critical Ningbo Fotile Kitchen Ware Co Ltd
Priority to CN202210928143.3A priority Critical patent/CN115430294B/en
Publication of CN115430294A publication Critical patent/CN115430294A/en
Application granted granted Critical
Publication of CN115430294B publication Critical patent/CN115430294B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D69/00Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D61/00Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/02Reverse osmosis; Hyperfiltration ; Nanofiltration
    • B01D61/027Nanofiltration
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D63/00Apparatus in general for separation processes using semi-permeable membranes
    • B01D63/06Tubular membrane modules
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D63/00Apparatus in general for separation processes using semi-permeable membranes
    • B01D63/10Spiral-wound membrane modules
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D69/00Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor
    • B01D69/12Composite membranes; Ultra-thin membranes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/442Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by nanofiltration
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds

Abstract

A roll-type nanofiltration membrane element capable of efficiently removing trace heavy metals comprises a central tube and a water purification membrane group wound on the central tube, and is characterized in that the water purification membrane group comprises a water inlet diversion net, a modified water production diversion cloth and a nanofiltration membrane which are folded and combined; the modified water-producing flow guide cloth is obtained by grafting acrylic acid on the surface of a non-woven fabric film and then reacting with organic amine. Through modifying the non-woven fabric, the non-woven fabric is aminated, and the removal rate of trace heavy metals in the water body can reach 99 percent or more.

Description

Roll type nanofiltration membrane element capable of efficiently removing trace heavy metals
Technical Field
The invention relates to a fiber membrane element for water body purification, in particular to a nanofiltration membrane element capable of adsorbing heavy metals.
Background
The main of the trace heavy metal that can high-efficiently get rid of in the water of filter membrane component on the existing market adopts reverse osmosis membrane, and general clearance is about 90%, and general nanofiltration membrane is about 83% to the clearance of trace heavy metal generally, and some adopt the composite filter core of receiving filtration, get rid of through adsorption or electrostatic action, if: adding graphene carbon material into the base membrane, grafting and crosslinking on the surface of the membrane to charge the membrane, and removing heavy metal through electrostatic action.
The RO membrane has low removal rate of heavy metals, cannot reach 99 percent removal rate, and has low retention of calcium and magnesium ions in water; the common nanofiltration membrane has low heavy metal removal rate and poor selectivity; the functional adsorption material generally relates to complex chemical reaction, has complicated steps, and some adsorption materials are adsorbed by physical acting force and are easy to desorb, so that secondary pollution is caused.
Disclosure of Invention
The invention aims to solve the technical problem of providing the roll-type nanofiltration membrane element capable of efficiently removing trace heavy metals aiming at the technical current situation.
The first technical solution adopted by the present invention to solve the above technical problems is: a roll-type nanofiltration membrane element capable of efficiently removing trace heavy metals comprises a central tube-level water purification membrane group wound on a central tube, and is characterized in that the water purification membrane group comprises a water inlet flow guide net, a modified water production flow guide cloth and a nanofiltration membrane, wherein the nanofiltration membrane is formed by folding and combining the nanofiltration membrane, the front surface of the nanofiltration membrane faces inwards, the nanofiltration membrane is divided and folded in half to form a water inlet flow channel, a crease end is flush with the central tube, a water production flow channel is formed between the upper surface and the lower surface of two adjacent membranes, and the other three sides of the two adjacent membranes except the side of the central tube are sealed by glue to form a nanofiltration membrane bag; the water inlet flow guide net is laid in the water inlet flow channel; the modified water production flow guide cloth is laid in the water production flow channel;
the modified water-producing flow guide cloth is obtained by grafting acrylic acid on the surface of a non-woven fabric film and then reacting with organic amine.
Preferably, the non-woven fabric film is at least one of polyethylene terephthalate, polybutylene terephthalate and polytrimethylene terephthalate.
Preferably, the grafted acrylic acid is prepared by the following steps: placing the non-woven fabric film in an irradiation bottle, adding acrylic acid grafting solution into the irradiation bottle to enable the non-woven fabric film or water-producing flow guide cloth to be completely soaked in the acrylic acid grafting solution, introducing nitrogen for protection for 15-20 min to remove oxygen in the bottle, sealing the irradiation bottle, placing the irradiation bottle in a constant-temperature sleeve container, and circulating water at the constant temperature of 26-28 ℃ in the constant-temperature sleeve to ensure that the temperature in the irradiation bottle is constant at 24-25 ℃. Then the whole set of equipment is placed in 7.4 x 10^14Bg 60 Irradiating in a Co radioactive source, wherein the absorption dose rate is 21.42Gy/min; and after the irradiation is finished, taking the non-woven fabric film out of the acrylic acid solution, cleaning to remove unpolymerized acrylic acid and acrylic acid homopolymer, draining the surface moisture after the cleaning is finished, drying the non-woven fabric film in a vacuum oven at 50-60 ℃ to constant weight, and sealing and storing to obtain the non-woven fabric film grafted with the acrylic acid.
Preferably, the acrylic acid graft solution is disposed as follows: adding ferrous sulfate heptahydrate and deionized water into a container, and stirring the mixture into a transparent solution according to the mass ratio of the ferrous sulfate heptahydrate to the deionized water of 1; and adding acrylic acid into the conical flask according to the mass ratio of the ferrous sulfate heptahydrate to the acrylic acid of 1-35, uniformly stirring, and sealing for later use to obtain the acrylic acid grafting solution.
Preferably, the non-woven fabric film is subjected to decontamination treatment before acrylic acid grafting, and the treatment mode is as follows: placing the non-woven fabric film in an acetone solution, heating to 56 ℃, and refluxing for 1h; taking out, airing, placing in a vacuum oven for drying at normal temperature, sealing and storing to obtain the non-woven fabric film without impurities.
The organic amine reaction conditions are as follows: the non-woven fabric film grafted with the acrylic acid is arranged in 1-10% organic amine solution and reacts for 10-48 h at 40-90 ℃, the non-woven fabric material is completely covered by the modification liquid, and the non-woven fabric film is taken out after the reaction is finished and is naturally dried after being washed for 2-10 h by pure water.
Preferably, the organic amine solution is aqueous solution of diethylenetriamine, triethylene tetramine, tetraethylenepentamine, pentaethylenehexamine or polyethyleneimine with the molecular weight of 600-70000.
The second technical solution adopted by the present invention to solve the above technical problems is: the spiral-wound nanofiltration membrane element is characterized in that the water purification membrane group comprises a water inlet flow guide net, a first produced water flow guide cloth, a second produced water flow guide cloth, a nanofiltration membrane and a modified non-woven fabric, wherein the first produced water flow guide cloth is wound on the central pipe, the modified non-woven fabric is wound on the central pipe, and finally the water inlet flow guide net, the second produced water flow guide cloth and the nanofiltration membrane are folded and combined to be wound on the central pipe; the water inlet flow guide net is laid in the water inlet flow channel; the second water production diversion cloth is laid in the water production flow channel;
the modified non-woven fabric is obtained by grafting acrylic acid on the surface of a non-woven fabric film and then reacting with organic amine.
Compared with the prior art, the invention has the advantages that: the non-woven fabric is aminated by modification, the removal rate of trace heavy metals in a water body can reach 99% or more, compared with a common roll-type nanofiltration membrane, the volume of the nanofiltration membrane is not obviously increased, complex modification or various compounding of a nanofiltration membrane is not needed, and the non-woven fabric has the function of efficiently removing trace heavy metal ions; the modified non-woven fabric only needs to be simply soaked, does not have the problem of slow falling or release, has simple process flow and lower cost, is easy to realize industrial production, and can be used in the field of water purification. The inlet non-woven fabric is modified through a low-cost and simple process, so that the common nanofiltration membrane has a function of efficiently removing heavy metals, and compared with the modified nanofiltration membrane on the market, the method for compounding other adsorption materials and the like is simple and efficient.
Drawings
Fig. 1 is a schematic structural diagram of embodiment 1.
Fig. 2 is a schematic structural diagram of embodiment 2.
Detailed Description
The invention is described in further detail below with reference to the following examples of the drawings.
In embodiment 1, as shown in fig. 1, the rolled nanofiltration membrane element capable of efficiently removing trace heavy metals in this embodiment includes a central tube 1 and a water purification membrane group wound on the central tube 1, where the water purification membrane group includes a water inlet flow guide net 2, a modified water production flow guide cloth 4, and a nanofiltration membrane 3, which are folded and combined together, the nanofiltration membrane 3 faces inward, is folded in half to form a water inlet flow channel, a fold end is flush with the central tube 1, a water production flow channel is formed between the upper and lower surfaces of two adjacent membranes, and the remaining three sides of the two adjacent membranes except the central tube side are sealed with glue to form a nanofiltration membrane bag; the water inlet flow guide net 2 is paved in the water inlet flow channel; the modified water producing flow guide cloth 4 is laid in the water producing flow passage; the modified water-producing flow-guiding cloth 4 is obtained by grafting acrylic acid on the surface of a non-woven fabric film and then reacting with organic amine.
The central tube 1 is a hollow but non-communicated central tube, the length of two sections of the inner part is about 1.
The other three sides of one nanofiltration membrane bag are sealed by glue, the sealing time is in the membrane rolling process, the nanofiltration membrane is placed, then glue is dispensed, and then the nanofiltration membrane is rolled into a filter element; the other three surfaces of the water inlet flow channel except the crease are not sealed, and one side of the two sides vertical to the central pipe is a raw water inlet, and the other end of the two sides is a concentrated water outlet; the ratio of the length of the long side of the water inlet flow guide net to the length of the long side of the nanofiltration membrane bag is 1.04-1.2; one water purification membrane group consists of 2 folded nanofiltration membranes. The modified water-producing flow guide cloth is made of polytrimethylene terephthalate.
The water producing flow guide cloth is grafted with acrylic acid by the following steps: and (3) arranging the produced water in an irradiation bottle in a diversion way, adding acrylic acid grafting liquid into the irradiation bottle to enable the produced water diversion cloth to be completely soaked into the acrylic acid grafting liquid, introducing nitrogen for protection for 20min to remove oxygen in the bottle, sealing the irradiation bottle, placing the irradiation bottle in a constant-temperature sleeve container, and circulating water at the constant temperature of 27 ℃ in the constant-temperature sleeve to ensure that the temperature in the irradiation bottle is constant at 24 ℃. Then the whole set of device is placed in a 60Co radioactive source with the radiation intensity of 7.4 x 10 Fa 14Bg for irradiation, wherein the absorption dose rate is 21.42Gy/min; and after the irradiation is finished, taking the water production guide cloth out of the acrylic acid solution, cleaning to remove unpolymerized acrylic acid and acrylic acid homopolymer, draining off surface water after the cleaning is finished, placing the non-woven fabric film in a vacuum oven at 55 ℃ to dry to constant weight, and sealing and storing to obtain the water production guide cloth grafted with the acrylic acid.
The acrylic acid grafting solution was prepared as follows: adding ferrous sulfate heptahydrate and deionized water into a container, and stirring the mixture into a transparent solution according to the mass ratio of the ferrous sulfate heptahydrate to the deionized water of 1; and adding acrylic acid into the conical flask according to the mass ratio of the ferrous sulfate heptahydrate to the acrylic acid of 1.
The water-producing flow guide cloth is subjected to impurity removal treatment before acrylic acid grafting, and the treatment mode is as follows: placing the water-producing diversion cloth in an acetone solution, heating to 56 ℃, and refluxing for 1h; taking out, airing, placing in a vacuum oven for drying at normal temperature, sealing and storing to obtain the water-producing diversion cloth with decontamination.
The organic amine reaction conditions are as follows: and (3) arranging the non-woven fabric film grafted with the acrylic acid in a 10% organic amine solution, reacting for 12 hours at 80 ℃, completely covering the water-producing flow guide cloth with the modified liquid, taking out after the reaction is finished, and naturally drying after pure water is washed for 3 hours. The organic amine solution is an aqueous solution of polyethyleneimine.
In the embodiment, the removal rate of trace heavy metals in the water body can reach 99% or more, and the types of the heavy metals in the embodiment mainly include cadmium ions, chromium ions, copper ions, lead ions, mercury ions, iron ions and manganese ions.
In embodiment 2, as shown in fig. 2, the rolled nanofiltration membrane element capable of efficiently removing trace heavy metals in this embodiment includes a central tube-level water purification membrane group wound around the central tube, the water purification membrane group includes a water inlet flow guide net 2, a first water production flow guide cloth 61, a second water production flow guide cloth 62, a nanofiltration membrane 3 and a modified nonwoven fabric 5, the first water production flow guide cloth 61 is firstly wound on the central tube 1, and the length of the first water production flow guide cloth is 20cm, so that the flux of a filter element can be increased; secondly, winding the modified non-woven fabric 5 on a central pipe, wherein the length of the modified non-woven fabric is 300cm; finally, the water inlet flow guide net 2, the second water production flow guide cloth 62 and the nanofiltration membrane 3 are folded and combined to be wound on the central pipe, the lengths of the water inlet flow guide net 2, the second water production flow guide cloth 62 and the nanofiltration membrane 3 are respectively 50cm, 53cm and 110cm, and the widths of the water inlet flow guide net 2, the second water production flow guide cloth 62 and the nanofiltration membrane 3 are all 26cm; the nanofiltration membrane 3 faces inwards, is divided and folded in half to form a water inlet flow channel, the fold line end is flush with the central pipe, a water production flow channel is formed between the upper surface and the lower surface of two adjacent membranes, the other three sides of the two adjacent membranes except the central pipe side are sealed by glue to form a nanofiltration membrane bag, and the nanofiltration membrane and a second water production diversion cloth which are carried with the water inlet diversion net are repeatedly placed until 3 nanofiltration membrane bags are formed; the water inlet flow guide net 2 is paved in the water inlet flow channel; the second water production flow guide cloth 62 is laid in the water production flow channel; the modified non-woven fabric 5 is obtained by grafting acrylic acid on the surface of a non-woven fabric film and then reacting with organic amine. The modified non-woven fabric material is polybutylene terephthalate.
The non-woven fabric grafting acrylic acid comprises the following steps: non-woven in an irradiation bottle, adding acrylic acid grafting liquid into the irradiation bottle to enable the water-producing diversion cloth to be completely soaked into the acrylic acid grafting liquid, introducing nitrogen for protection for 15min to remove oxygen in the bottle, sealing the irradiation bottle, placing the irradiation bottle in a constant-temperature sleeve container, and circulating water at the constant temperature of 28 ℃ in the constant-temperature sleeve to ensure that the temperature in the irradiation bottle is constant at 25 ℃. Then the whole set of device is placed in 7.4 x 10^14Bg 60 Irradiating in a Co radioactive source, wherein the absorption dose rate is 21.42Gy/min; after the irradiation is finished, taking out the non-woven fabric from the acrylic acid solutionAnd then, cleaning to remove unpolymerized acrylic acid and acrylic acid homopolymer, draining the surface moisture after cleaning, placing the non-woven fabric film in a vacuum oven at 60 ℃ to dry to constant weight, and sealing and storing to obtain the non-woven fabric grafted with acrylic acid.
The acrylic acid grafting solution was prepared as follows: adding ferrous sulfate heptahydrate and deionized water into a container, and stirring the mixture into a transparent solution according to the mass ratio of the ferrous sulfate heptahydrate to the deionized water of 1; and adding acrylic acid into the conical flask according to the mass ratio of the ferrous sulfate heptahydrate to the acrylic acid of 1.
The non-woven fabric is subjected to decontamination treatment before acrylic acid grafting, and the treatment mode is as follows: placing the non-woven fabric in an acetone solution, heating to 56 ℃, and refluxing for 1h; taking out, air drying, placing in a vacuum oven, drying at normal temperature, sealing, and storing to obtain nonwoven fabric with impurity removed.
The organic amine reaction conditions are as follows: and (3) arranging the non-woven fabric film grafted with the acrylic acid in a 1% organic amine solution, reacting for 18h at 90 ℃, completely covering the non-woven fabric with the modification solution, taking out after the reaction is finished, and naturally drying after cleaning for 1h with pure water. The organic amine solution is an aqueous solution of polyethyleneimine.

Claims (10)

1. A roll-type nanofiltration membrane element capable of efficiently removing trace heavy metals comprises a central tube-level water purification membrane group wound on a central tube, and is characterized in that the water purification membrane group comprises a water inlet flow guide net, a modified water production flow guide cloth and a nanofiltration membrane, wherein the nanofiltration membrane is formed by folding and combining the nanofiltration membrane, the front surface of the nanofiltration membrane faces inwards, the nanofiltration membrane is divided and folded in half to form a water inlet flow channel, a crease end is flush with the central tube, a water production flow channel is formed between the upper surface and the lower surface of two adjacent membranes, and the other three sides of the two adjacent membranes except the side of the central tube are sealed by glue to form a nanofiltration membrane bag; the water inlet flow guide net is paved in the water inlet flow channel; the modified water production flow guide cloth is laid in the water production flow channel;
the modified water-producing flow guide cloth is obtained by grafting acrylic acid on the surface of a non-woven fabric film and then reacting with organic amine.
2. The roll-type nanofiltration membrane element capable of efficiently removing trace heavy metals according to claim 1, wherein the non-woven fabric film is at least one of polyethylene terephthalate, polybutylene terephthalate, or polytrimethylene terephthalate.
3. The roll-type nanofiltration membrane element capable of efficiently removing trace heavy metals according to claim 1, wherein the grafting acrylic acid comprises the following steps: placing the non-woven fabric film in an irradiation bottle, adding acrylic acid grafting solution into the irradiation bottle to enable the non-woven fabric film or water-producing flow guide cloth to be completely soaked in the acrylic acid grafting solution, introducing nitrogen for protection for 15-20 min to remove oxygen in the bottle, sealing the irradiation bottle, placing the irradiation bottle in a constant-temperature sleeve container, and circulating water at the constant temperature of 26-28 ℃ in the constant-temperature sleeve to ensure that the temperature in the irradiation bottle is constant at 24-25 ℃. Then the whole set of equipment is placed in 7.4 x 10^14Bg 60 Irradiating in a Co radioactive source, wherein the absorption dose rate is 21.42Gy/min; and after the irradiation is finished, taking the non-woven fabric film out of the acrylic acid solution, cleaning to remove unpolymerized acrylic acid and acrylic acid homopolymer, draining off surface moisture after the cleaning is finished, drying the non-woven fabric film in a vacuum oven at 50-60 ℃ to constant weight, sealing and storing to obtain the non-woven fabric film grafted with the acrylic acid.
4. The rolled nanofiltration membrane element capable of efficiently removing trace heavy metals according to claim 3, wherein the acrylic acid grafting solution is prepared in the following manner: adding ferrous sulfate heptahydrate and deionized water into a container, and stirring the mixture into a transparent solution according to the mass ratio of the ferrous sulfate heptahydrate to the deionized water of 1; and adding acrylic acid into the conical flask according to the mass ratio of the ferrous sulfate heptahydrate to the acrylic acid of 1-35, uniformly stirring, and sealing for later use to obtain the acrylic acid grafting solution.
5. The roll-type nanofiltration membrane element capable of efficiently removing trace heavy metals according to claim 3, wherein the non-woven fabric film is subjected to decontamination treatment before acrylic acid grafting, and the treatment method comprises the following steps: placing the non-woven fabric film in an acetone solution, heating to 56 ℃, and refluxing for 1h; taking out, airing, placing in a vacuum oven for drying at normal temperature, sealing and storing to obtain the non-woven fabric film without impurities.
6. The roll-type nanofiltration membrane element capable of efficiently removing trace heavy metals according to claim 1, wherein the organic amine reaction conditions are as follows:
the non-woven fabric film grafted with the acrylic acid is arranged in 1-10% organic amine solution and reacts for 10-48 h at 40-90 ℃, the non-woven fabric material is completely covered by the modification liquid, and the non-woven fabric film is taken out after the reaction is finished and is naturally dried after being washed for 2-10 h by pure water.
7. The roll-type nanofiltration membrane element capable of efficiently removing trace heavy metals according to claim 6, wherein the organic amine solution is diethylenetriamine, triethylenetetramine, tetraethylenepentamine, pentaethylenehexamine or an aqueous solution of polyethyleneimine with a molecular weight of 600-70000.
8. The spiral-wound nanofiltration membrane element is characterized in that the water purification membrane group comprises a water inlet flow guide net, a first produced water flow guide cloth, a second produced water flow guide cloth, a nanofiltration membrane and a modified non-woven fabric, wherein the first produced water flow guide cloth is wound on the central pipe, the modified non-woven fabric is wound on the central pipe, and finally the water inlet flow guide net, the second produced water flow guide cloth and the nanofiltration membrane are folded and combined to be wound on the central pipe; the water inlet flow guide net is laid in the water inlet flow channel; the second water production diversion cloth is laid in the water production flow channel;
the modified non-woven fabric is obtained by grafting acrylic acid on the surface of a non-woven fabric film and then reacting the non-woven fabric film with organic amine.
9. The rolled nanofiltration membrane element capable of efficiently removing trace heavy metals according to claim 8, wherein the grafting of acrylic acid comprises the following steps: placing a non-woven fabric film in an irradiation bottle, adding acrylic acid grafting solution into the irradiation bottle to completely soak the non-woven fabric film or water-producing diversion cloth into the acrylic acid grafting solution, introducing nitrogen for protection for 15-20 min to remove oxygen in the bottle, sealing the irradiation bottle, placing the bottle in a constant-temperature sleeve container, and circulating water at the constant temperature of 26-28 ℃ in the constant-temperature sleeve to ensure that the temperature in the irradiation bottle is constant at 24-25 ℃. Then the whole set of device is placed in 7.4 x 10^14Bg 60 Irradiating in a Co radioactive source, wherein the absorption dose rate is 21.42Gy/min; and after the irradiation is finished, taking the non-woven fabric film out of the acrylic acid solution, cleaning to remove unpolymerized acrylic acid and acrylic acid homopolymer, draining the surface moisture after the cleaning is finished, drying the non-woven fabric film in a vacuum oven at 50-60 ℃ to constant weight, and sealing and storing to obtain the non-woven fabric film grafted with the acrylic acid.
10. The roll-type nanofiltration membrane element capable of efficiently removing trace heavy metals according to claim 8, wherein the organic amine reaction conditions are as follows:
the non-woven fabric film grafted with the acrylic acid is arranged in 1-10% organic amine solution and reacts for 10-48 h at 40-90 ℃, the non-woven fabric material is completely covered by the modification liquid, and the non-woven fabric film is taken out after the reaction is finished and is naturally dried after being washed for 2-10 h by pure water.
CN202210928143.3A 2022-08-03 2022-08-03 Rolling nanofiltration membrane element capable of efficiently removing trace heavy metals Active CN115430294B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202210928143.3A CN115430294B (en) 2022-08-03 2022-08-03 Rolling nanofiltration membrane element capable of efficiently removing trace heavy metals

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202210928143.3A CN115430294B (en) 2022-08-03 2022-08-03 Rolling nanofiltration membrane element capable of efficiently removing trace heavy metals

Publications (2)

Publication Number Publication Date
CN115430294A true CN115430294A (en) 2022-12-06
CN115430294B CN115430294B (en) 2024-04-02

Family

ID=84243162

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202210928143.3A Active CN115430294B (en) 2022-08-03 2022-08-03 Rolling nanofiltration membrane element capable of efficiently removing trace heavy metals

Country Status (1)

Country Link
CN (1) CN115430294B (en)

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH11279945A (en) * 1998-03-23 1999-10-12 Japan Atom Energy Res Inst Polyethylene material graft-polymerized with radiation
CN102102295A (en) * 2010-11-26 2011-06-22 昆明理工大学 Ion exchange nonwoven fabric with high carboxyl content and preparation method thereof
CN102965929A (en) * 2012-10-12 2013-03-13 苏州大学 Preparation method and application of modified polypropylene non-woven fabric
CN103147291A (en) * 2013-01-18 2013-06-12 中国科学院上海应用物理研究所 Grafted copolymer with modified amino and preparation method and application thereof
CN108744984A (en) * 2018-05-16 2018-11-06 南京帝膜净水材料开发有限公司 A kind of wound membrane element
CN114082310A (en) * 2022-01-20 2022-02-25 湖南叶之能科技有限公司 Roll type membrane element and preparation method and application thereof

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH11279945A (en) * 1998-03-23 1999-10-12 Japan Atom Energy Res Inst Polyethylene material graft-polymerized with radiation
CN102102295A (en) * 2010-11-26 2011-06-22 昆明理工大学 Ion exchange nonwoven fabric with high carboxyl content and preparation method thereof
CN102965929A (en) * 2012-10-12 2013-03-13 苏州大学 Preparation method and application of modified polypropylene non-woven fabric
CN103147291A (en) * 2013-01-18 2013-06-12 中国科学院上海应用物理研究所 Grafted copolymer with modified amino and preparation method and application thereof
CN108744984A (en) * 2018-05-16 2018-11-06 南京帝膜净水材料开发有限公司 A kind of wound membrane element
CN114082310A (en) * 2022-01-20 2022-02-25 湖南叶之能科技有限公司 Roll type membrane element and preparation method and application thereof

Also Published As

Publication number Publication date
CN115430294B (en) 2024-04-02

Similar Documents

Publication Publication Date Title
CN106076283B (en) A kind of nano-cellulose/poly-dopamine hydrogel adsorbent and the preparation method and application thereof
Xu et al. A recyclable phosphinic acid functionalized polyacrylonitrile fiber for selective and efficient removal of Hg2+
Awual et al. Arsenate removal from water by a weak-base anion exchange fibrous adsorbent
Gu et al. Fabrication of hierarchically porous NH2-MIL-53/wood-carbon hybrid membrane for highly effective and selective sequestration of Pb2+
CN108479712B (en) Modified carbon nanotube film material capable of adsorbing and degrading tetrabromobisphenol A and application method thereof
Nthunya et al. Adsorption of phenolic compounds by polyacrylonitrile nanofibre membranes: A pretreatment for the removal of hydrophobic bearing compounds from water
CN105080509A (en) Nanofiber membrane and membrane adsorbing assembly for extracting uranium from seawater and brine water and application of nanofiber membrane and membrane adsorbing assembly
Pramanik et al. 3‑Mercapto‑propanoic acid modified cellulose filter paper for quick removal of arsenate from drinking water
Wang et al. Novel amidoxime-functionalized SBA-15-incorporated polymer membrane-type adsorbent for uranium extraction from wastewater
Teng et al. A green hydrothermal synthesis of polyacrylonitrile@ carbon/MIL-101 (Fe) composite nanofiber membrane for efficient selective removal of tetracycline
CN115430294A (en) Roll type nanofiltration membrane element capable of efficiently removing trace heavy metals
WO1999056850A1 (en) Chelate-forming filter, process for producing the same, and method of purifying liquid with the filter
CN103495399A (en) Preparation method and application of sludge activated carbon
Wang et al. Efficient removal of arsenate from water using electrospun polyethylenimine/polyvinyl chloride nanofiber sheets
Wang et al. Fabrication of P (AN-MA)/rGO-g-PAO superhydrophilic nanofiber membrane for removal of heavy metal ions
Lu et al. Polyphosphonate-segmented macroporous organosilicon frameworks for efficient dynamic enrichment of uranium with in-situ regeneration
CN116240674A (en) Preparation method of magnetic nanofiber membrane
CN116219634A (en) Preparation method of nanofiber membrane with covalent organic framework
JP2013061220A (en) Radioactive cesium adsorptive cloth
CN114887434B (en) VOCs treatment process for finished oil
JP3723225B2 (en) Chelate-forming fibers, their production and use
CN113813923B (en) Continuous ZIF-8 membrane material and preparation method thereof
CN109281063B (en) Preparation method and application of organic silicon fiber membrane containing secondary amino group
CN115573096A (en) Preparation method of polyurethane nanofiber membrane
CN110975841B (en) Magnetic polymer nano-adsorption material LM-MP and preparation method and application thereof

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