CN110237806A - Cu- attapulgite-NH2The preparation method of composite material and its application in Adsorption of Radioactive water body in iodide ion - Google Patents

Cu- attapulgite-NH2The preparation method of composite material and its application in Adsorption of Radioactive water body in iodide ion Download PDF

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Publication number
CN110237806A
CN110237806A CN201910431875.XA CN201910431875A CN110237806A CN 110237806 A CN110237806 A CN 110237806A CN 201910431875 A CN201910431875 A CN 201910431875A CN 110237806 A CN110237806 A CN 110237806A
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attapulgite
composite material
preparation
adsorption
water body
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CN110237806B (en
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茆平
孙爱武
余祥坤
钱国庆
赵雨露
张静
蒋金龙
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Huaiyin Institute of Technology
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/10Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
    • B01J20/12Naturally occurring clays or bleaching earth
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28014Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their form
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • 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
    • C02F2101/12Halogens or halogen-containing compounds

Abstract

The present invention relates to dirty water decontamination handles technical fields, disclose a kind of Cu- attapulgite-NH for iodide ion absorption2The preparation method of composite material and its application in Adsorption of Radioactive water body in iodide ion, method includes the following steps: S1: dispersing Acid-treatment Palygorskite Clays in copper nitrate solution, after stirring impregnates for 24 hours at 40 DEG C, centrifugation, washing, drying, it is then dispersed in organic solvent-water mixed solution, it is subsequently added into formic acid and ammonium hydroxide, hydro-thermal reaction prepares Cu- attapulgite material;S2: dispersing the Cu- attapulgite material in aqueous solution, dioctadecyldimethylammonium bromide is added, after being sufficiently stirred, hydro-thermal reaction prepares Cu- attapulgite-NH2Composite material.Compared with prior art, the present invention improves the adsorption capacity and selectivity of existing copper-based adsorbent, and the removing for radioiodine in waste water provides Technical Reference.

Description

Cu- attapulgite-NH2The preparation method of composite material and its in Adsorption of Radioactive water body Application in middle iodide ion
Technical field
The present invention relates to dirty water decontamination handles technical field, in particular to a kind of Cu- attapulgite-NH2Composite material Preparation method and its application in Adsorption of Radioactive water body in iodide ion.
Background technique
With flourishing for China's economic and becoming increasingly conspicuous for environmental problem, Nuclear Power Industry has become the important hair of country Exhibition strategy, it is contemplated that run to the year two thousand twenty China nuclear power and be up to 88 GW building installation total amount.Consequent is effectively solved to put Pollution is penetrated to be of great significance to the safe handling of nuclear energy.The breakage monitoring that radioiodine is often used as Reactor fuel element cladding The signal radionuclide of environmental monitoring after index and nuclear explosion, is one of inevitable outcome of nuclear fission.Thus, efficiently remove liquid phase radiation Property iodine to be Nuclear Safety utilize institute's key scientific problems to be solved.
The technologies such as chemical precipitation, porous material absorption, ion exchange and UF membrane can be used for the removal of liquid phase radioiodine It uses.The metal material that chemical precipitation uses is expensive and be easy to cause the secondary pollution of heavy metal.Porous material is in complexity The selective absorption efficiency of environment is difficult to ensure.Due to the use of organic or inorganic solvent, so that ion exchange technique also easily produces Raw secondary pollution.Though membrane separation technique possesses good removal efficiency, operating cost is costly.
Summary of the invention
Goal of the invention: aiming at the problems existing in the prior art, the present invention provides a kind of Cu- attapulgite-NH2Composite wood The preparation method of material and its application in Adsorption of Radioactive water body in iodide ion utilize the charge characteristic object of composite material surface Reason absorption liquid phase radioactive pollutant, using Cu selective absorption radioiodine, more traditional copper-based adsorbent improves iodine absorption Capacity and selectivity, the removing for radioiodine in waste water provide Technical Reference.
Technical solution: the present invention provides a kind of Cu- attapulgite-NH2The preparation method of composite material, including following step Rapid: S1: dispersing Acid-treatment Palygorskite Clays in copper nitrate solution, and at 40 DEG C after 24 h of stirring dipping, centrifugation, is dried at washing It is dry, it is then dispersed in organic solvent-water mixed solution, is subsequently added into formic acid and ammonium hydroxide, hydro-thermal reaction prepares Cu- bumps Stick stone material;S2: dispersing the Cu- attapulgite material in aqueous solution, and dioctadecyldimethylammonium bromide is added, fills After dividing stirring, hydro-thermal reaction prepares Cu- attapulgite-NH2Composite material.
Preferably, in the S1, the Acid-treatment Palygorskite Clays, the copper nitrate solution, the formic acid and institute The mass ratio for stating ammonium hydroxide is 1:0.01 ~ 0.10:0.05 ~ 3.0:1.0 ~ 8.0.
Preferably, in the S1, the temperature of the hydro-thermal reaction is 150 oC, and the reaction time is 2 h.
Preferably, in the S2, the matter of the Cu- attapulgite material and the dioctadecyldimethylammonium bromide Amount is than being 1:1 ~ 10.
Preferably, in the S2, the temperature of the hydro-thermal reaction is 120 oC, and the reaction time is 2 h.
Preferably, in the S1, the Acid-treatment Palygorskite Clays the preparation method is as follows:
Preferably, in deionized water by attapulgite clay dispersion, stirring is placed in dilute hydrochloric acid and impregnates after being centrifuged decontamination, Agitated and dispersion, is made the acidification attapulgite;It is lyophilized after washing spare.
Preferably, in the S1, the mixed solution of the organic solvent-water is that the alcohol-water that mass fraction is 60% is mixed Close solution.
The present invention also provides a kind of Cu- attapulgite-NH2Composite material is in Adsorption of Radioactive water body in iodide ion Using.
Preferably, the concentration of iodide ion is 0.1 ~ 1.0 mM in the radioactivity water body;Cu- attapulgite-the NH2It is multiple Injected volume of the condensation material in the radioactivity water body is 0.5 ~ 2 gL- 1
Preferably, the Cu- attapulgite-NH2Composite material in the radioactivity water body adsorb when temperature be 25 ~ 50 oC, adsorption time are 0.5 ~ 24 h.
The utility model has the advantages that the present invention Features of Attapulgite Minerals good, cheap and big specific surface using stability is as matrix material Copper nitrate, is carried in attapulgite duct with infusion process, is redispersed in solution, using hydrothermal synthesis method, with formic acid by material Cu- attapulgite composite material is restored and regulated and controled with ammonium hydroxide.It again disperses above-mentioned composite material in solution, is added double 18 Alkyl dimethyl bromination ammonium surfactant regulates and controls attapulgite surface charge, prepares Cu- attapulgite-through hydro-thermal reaction NH2Composite material.
Cu- attapulgite-the NH that will be prepared2Composite material is for the iodide ion in Adsorption of Radioactive water body, by ammonia (attapulgite original tape has negative electrical charge to the positive charge characteristic on attapulgite surface, after amido modified, makes its surface band after base modification Positive charge is more advantageous to the absorption of anion-iodide ion), the low concentration iodide ion in enrichment solution recycles in composite material Cu reacted with the CuO compacted zone on surface generate Cu2O is reacted with iodide ion generates cuprous iodide.In adsorption process, due to object Reason absorption and chemisorption synergistic effect, so that Cu- attapulgite-NH2The more traditional copper-based adsorbent of composite material has higher Adsorption capacity.
Compared with prior art, remarkable advantage is: (1) this method use simple hydrothermal synthesis method, simple process, Generated time is short, and raw material are cheap and easy to get, nontoxic;(2) Cu synthesized is located in the duct of attapulgite, avoids in adsorption process Cu's falls off;(3) adsorbent is cheap, is conducive to practical application.
Detailed description of the invention
Fig. 1 is the Cu- attapulgite-NH prepared in embodiment 12The SEM scanning electron microscope (SEM) photograph of composite material;
Fig. 2 is the Cu- attapulgite-NH prepared in embodiment 12Composite material absorption property curve graph;
Fig. 3 is the Cu- attapulgite-NH prepared in embodiment 12The SEM scanning electron microscope (SEM) photograph of composite material;
Fig. 4 is the Cu- attapulgite-NH prepared in embodiment 12Composite material absorption property curve graph;
Fig. 5 is the Cu- attapulgite-NH prepared in embodiment 12The SEM scanning electron microscope (SEM) photograph of composite material;
Fig. 6 is the Cu- attapulgite-NH prepared in embodiment 12Composite material absorption property curve graph.
Specific embodiment
The present invention is described in detail with reference to the accompanying drawing.
Embodiment 1:
Present embodiments provide for a kind of Cu- attapulgite-NH2The preparation method of composite material, comprising the following steps:
The preparation of Acid-treatment Palygorskite Clays: in deionized water by attapulgite clay dispersion, stirring, after being centrifuged decontamination, It is placed in dilute hydrochloric acid and impregnates, acidification attapulgite is made in agitated and dispersion;It is lyophilized after washing spare.
The preparation of Cu- attapulgite material: 40 mL, 0.1 M is dispersed by the acidification attapulgite material after 1 g purification In copper nitrate solution, after stirring impregnates for 24 hours at 40 DEG C, after centrifugation, washing three times, 100 oC drying.Transfer to hydro-thermal reaction Kettle, using dispersing in 60% alcohol-water mixed solution, 2 mL formic acid, the 4 mL ammonium hydroxide of addition, after 150 oC hydro-thermal reaction, 2 h, Prepare Cu- attapulgite material.
Cu- attapulgite-NH2The preparation of composite material: it is water-soluble that 40 mL are dispersed by the above-mentioned Cu- attapulgite material of 1 g In liquid, 4 g dioctadecyldimethylammonium bromide are added, after being sufficiently stirred, are transferred in hydrothermal reaction kettle, 120 oC hydro-thermals are anti- It answers after 2 h to get Cu- attapulgite-NH2Composite material.
Cu- attapulgite-the NH being prepared2The SEM Electronic Speculum of composite material is as shown in Figure 1.It can be seen that compound after preparation Material is able to maintain the original club shaped structure of attapulgite.
By 50 mg Cu- attapulgite-NH obtained above2The simulated emission of composite material addition 50 mL, 1.0 mM In the solution of iodide ion, at normal temperature, after adsorbing 30 min, filtering detects residual iodine ions concentration in solution.
As the absorption result of Fig. 2 shows Cu- attapulgite-NH2Composite material reaches adsorption equilibrium in 10 h, absorption Efficiency can reach 75%, and adsorption capacity reaches 0.75 mmol/g.
Embodiment 2:
Present embodiments provide for a kind of Cu- attapulgite-NH2The preparation method of composite material, comprising the following steps:
It is acidified the preparation of attapulgite: it is identical with embodiment 1, it is not repeated herein.
The preparation of Cu- attapulgite material: 40 mL, 0.01 M is dispersed by the acidification attapulgite material after 1 g purification In copper nitrate solution, after stirring impregnates for 24 hours at 40 DEG C, after centrifugation, washing three times, 100 oC drying.Transfer to hydro-thermal reaction Kettle, using dispersing in 60% alcohol-water mixed solution, 0.05 mL formic acid, the 1 mL ammonium hydroxide of addition, 150 oC hydro-thermal reaction, 2 h Afterwards, Cu- attapulgite material is prepared.
Cu- attapulgite-NH2The preparation of composite material: it is water-soluble that 40 mL are dispersed by the above-mentioned Cu- attapulgite material of 1 g In liquid, 2 g dioctadecyldimethylammonium bromide are added, after being sufficiently stirred, are transferred in hydrothermal reaction kettle, 120 oC hydro-thermals are anti- It answers after 2 h to get Cu- attapulgite-NH2Composite material.
Cu- attapulgite-the NH being prepared2The SEM Electronic Speculum of composite material is as shown in Figure 3.It can be seen that compound after preparation Material is able to maintain the original club shaped structure of attapulgite.
By 50 mg Cu- attapulgite-NH obtained above2The simulated emission of composite material addition 20 mL, 1.0 mM In the solution of iodide ion, at normal temperature, after adsorbing 30 min, filtering detects residual iodine ions concentration in solution.
As the absorption result of Fig. 4 shows Cu- attapulgite-NH2Composite material reaches adsorption equilibrium in 2 h, absorption Efficiency can reach 60%, and adsorption capacity reaches 0.24 mmol/g.
Embodiment 3:
Present embodiments provide for a kind of Cu- attapulgite-NH2The preparation method of composite material, comprising the following steps:
It is acidified the preparation of attapulgite: it is identical with embodiment 1, it is not repeated herein.
The preparation of Cu- attapulgite material: 40 mL, 0.12 M is dispersed by the acidification attapulgite material after 1 g purification In copper nitrate solution, after stirring impregnates for 24 hours at 40 DEG C, after centrifugation, washing three times, 100 oC drying.Transfer to hydro-thermal reaction Kettle, using dispersing in 60% alcohol-water mixed solution, 3 mL formic acid, the 6 mL ammonium hydroxide of addition, after 150 oC hydro-thermal reaction, 2 h, Prepare Cu- attapulgite material.
Cu- attapulgite-NH2The preparation of composite material: it is water-soluble that 40 mL are dispersed by the above-mentioned Cu- attapulgite material of 1 g In liquid, 8 g dioctadecyldimethylammonium bromide are added, after being sufficiently stirred, are transferred in hydrothermal reaction kettle, 120 oC hydro-thermals are anti- It answers after 2 h to get Cu- attapulgite-NH2Composite material.
Cu- attapulgite-the NH being prepared2The SEM Electronic Speculum of composite material is as shown in Figure 5.It can be seen that compound after preparation Material is able to maintain the original club shaped structure of attapulgite, but it is more serious to reunite.
By 50 mg Cu- attapulgite-NH obtained above2The simulated emission of composite material addition 80 mL, 1.0 mM In the solution of iodide ion, at normal temperature, after adsorbing 30 min, filtering detects residual iodine ions concentration in solution.
As the absorption result of Fig. 6 shows Cu- attapulgite-NH2Composite material reaches adsorption equilibrium in 12 h, absorption Efficiency can reach 45%, and adsorption capacity reaches 0.72 mmol/g.
The technical concepts and features of above embodiment only to illustrate the invention, its object is to allow be familiar with technique People cans understand the content of the present invention and implement it accordingly, and it is not intended to limit the scope of the present invention.It is all according to the present invention The equivalent transformation or modification that Spirit Essence is done, should be covered by the protection scope of the present invention.

Claims (10)

1. a kind of Cu- attapulgite-NH2The preparation method of composite material, which comprises the following steps:
S1: dispersing Acid-treatment Palygorskite Clays in copper nitrate solution, and after stirring impregnates for 24 hours at 40 DEG C, centrifugation, is dried at washing It is dry, it is then dispersed in organic solvent-water mixed solution, is subsequently added into formic acid and ammonium hydroxide, hydro-thermal reaction prepares Cu- bumps Stick stone material;
S2: dispersing the Cu- attapulgite material in aqueous solution, and dioctadecyldimethylammonium bromide is added, sufficiently stirs After mixing, hydro-thermal reaction prepares Cu- attapulgite-NH2Composite material.
2. Cu- attapulgite-NH according to claim 12The preparation method of composite material, which is characterized in that in the S1 In, the Acid-treatment Palygorskite Clays, the copper nitrate solution, the formic acid and the ammonium hydroxide mass ratio be 1:0.01 ~ 0.10:0.05 ~ 3.0:1.0 ~ 8.0.
3. Cu- attapulgite-NH according to claim 12The preparation method of composite material, which is characterized in that described In S1, the temperature of the hydro-thermal reaction is 150 oC, and the reaction time is 2 h.
4. Cu- attapulgite-NH according to claim 12The preparation method of composite material, which is characterized in that in the S2 In, the mass ratio of the Cu- attapulgite material and the dioctadecyldimethylammonium bromide is 1:1 ~ 10.
5. Cu- attapulgite-NH according to claim 12The preparation method of composite material, which is characterized in that in the S2 In, the temperature of the hydro-thermal reaction is 120 oC, and the reaction time is 2 h.
6. Cu- attapulgite-NH according to any one of claim 1 to 52The preparation method of composite material, feature exist In, in the S1, the Acid-treatment Palygorskite Clays the preparation method is as follows:
In deionized water by attapulgite clay dispersion, stirring is placed in dilute hydrochloric acid and impregnates after being centrifuged decontamination, agitated And dispersion, the acidification attapulgite is made;It is lyophilized after washing spare.
7. Cu- attapulgite-NH according to any one of claim 1 to 52The preparation method of composite material, feature exist In in the S1, the mixed solution of the organic solvent-water is the alcohol-water mixed solution that mass fraction is 60%.
8. a kind of Cu- attapulgite-NH as described in any one of claims 1 to 72Composite material is in Adsorption of Radioactive water body Application in middle iodide ion.
9. Cu- attapulgite-NH according to claim 82Composite material answering in iodide ion in Adsorption of Radioactive water body With, which is characterized in that the concentration of iodide ion is 0.1 ~ 1.0 mM in the radioactivity water body;Cu- attapulgite-the NH2It is multiple Injected volume of the condensation material in the radioactivity water body is 0.5 ~ 2gL- 1
10. Cu- attapulgite-NH according to claim 82Composite material is in Adsorption of Radioactive water body in iodide ion Using, which is characterized in that the Cu- attapulgite-NH2Composite material in the radioactivity water body adsorb when temperature be 25 ~ 50 oC, adsorption time are 0.5 ~ 24 h.
CN201910431875.XA 2019-05-23 2019-05-23 Cu-Attapulgite-NH2Preparation method of composite material and application of composite material in adsorption of iodine ions in radioactive water Active CN110237806B (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114259986A (en) * 2021-12-28 2022-04-01 淮阴工学院 Preparation method of magnetic activated carbon-red mud-attapulgite composite adsorbent
CN114345301A (en) * 2022-01-19 2022-04-15 西南科技大学 Preparation and application of Bi @ chrysotile aerogel for removing radioactive iodine gas and aerosol
CN117299068A (en) * 2023-10-08 2023-12-29 保山学院 Preparation method of copper-based carbon silicon material and application of copper-based carbon silicon material in adsorption of radioactive iodine
CN117299068B (en) * 2023-10-08 2024-04-30 保山学院 Preparation method of copper-based carbon silicon material and application of copper-based carbon silicon material in adsorption of radioactive iodine

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Publication number Priority date Publication date Assignee Title
CN102284274A (en) * 2011-06-07 2011-12-21 天津大学 Preparation method for modified montmorillonite adsorbent and application thereof to removing micro or trace iodine
CN104941584A (en) * 2015-07-06 2015-09-30 河北工业大学 SiO2/C composite material for adsorbing heavy metal ions in water body and application thereof
CN106824084A (en) * 2017-03-15 2017-06-13 天津大学 The preparation method of the carbon-supported catalyst of a kind of nano cuprous oxide/copper modification and except iodine application

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102284274A (en) * 2011-06-07 2011-12-21 天津大学 Preparation method for modified montmorillonite adsorbent and application thereof to removing micro or trace iodine
CN104941584A (en) * 2015-07-06 2015-09-30 河北工业大学 SiO2/C composite material for adsorbing heavy metal ions in water body and application thereof
CN106824084A (en) * 2017-03-15 2017-06-13 天津大学 The preparation method of the carbon-supported catalyst of a kind of nano cuprous oxide/copper modification and except iodine application

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114259986A (en) * 2021-12-28 2022-04-01 淮阴工学院 Preparation method of magnetic activated carbon-red mud-attapulgite composite adsorbent
CN114259986B (en) * 2021-12-28 2023-06-30 淮阴工学院 Preparation method of magnetic activated carbon-red mud-attapulgite composite adsorbent
CN114345301A (en) * 2022-01-19 2022-04-15 西南科技大学 Preparation and application of Bi @ chrysotile aerogel for removing radioactive iodine gas and aerosol
CN114345301B (en) * 2022-01-19 2023-09-08 西南科技大学 Preparation and application of Bi@ chrysotile aerogel for removing radioactive iodine gas and aerosol
CN117299068A (en) * 2023-10-08 2023-12-29 保山学院 Preparation method of copper-based carbon silicon material and application of copper-based carbon silicon material in adsorption of radioactive iodine
CN117299068B (en) * 2023-10-08 2024-04-30 保山学院 Preparation method of copper-based carbon silicon material and application of copper-based carbon silicon material in adsorption of radioactive iodine

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