CN117987211A - Radioactive decontamination foam-based eutectic solvent and preparation method and application thereof - Google Patents

Radioactive decontamination foam-based eutectic solvent and preparation method and application thereof Download PDF

Info

Publication number
CN117987211A
CN117987211A CN202410148804.XA CN202410148804A CN117987211A CN 117987211 A CN117987211 A CN 117987211A CN 202410148804 A CN202410148804 A CN 202410148804A CN 117987211 A CN117987211 A CN 117987211A
Authority
CN
China
Prior art keywords
foam
eutectic solvent
hydrogen bond
acid
based eutectic
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN202410148804.XA
Other languages
Chinese (zh)
Inventor
王志鹏
汤奇龙
徐超
董雪
郝怀欣
陈靖
王建晨
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.)
Tsinghua University
Original Assignee
Tsinghua University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Tsinghua University filed Critical Tsinghua University
Priority to CN202410148804.XA priority Critical patent/CN117987211A/en
Publication of CN117987211A publication Critical patent/CN117987211A/en
Pending legal-status Critical Current

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
    • CCHEMISTRY; METALLURGY
    • C11ANIMAL OR VEGETABLE OILS, FATS, FATTY SUBSTANCES OR WAXES; FATTY ACIDS THEREFROM; DETERGENTS; CANDLES
    • C11DDETERGENT COMPOSITIONS; USE OF SINGLE SUBSTANCES AS DETERGENTS; SOAP OR SOAP-MAKING; RESIN SOAPS; RECOVERY OF GLYCEROL
    • C11D1/00Detergent compositions based essentially on surface-active compounds; Use of these compounds as a detergent
    • C11D1/02Anionic compounds
    • C11D1/04Carboxylic acids or salts thereof
    • CCHEMISTRY; METALLURGY
    • C11ANIMAL OR VEGETABLE OILS, FATS, FATTY SUBSTANCES OR WAXES; FATTY ACIDS THEREFROM; DETERGENTS; CANDLES
    • C11DDETERGENT COMPOSITIONS; USE OF SINGLE SUBSTANCES AS DETERGENTS; SOAP OR SOAP-MAKING; RESIN SOAPS; RECOVERY OF GLYCEROL
    • C11D17/00Detergent materials or soaps characterised by their shape or physical properties
    • C11D17/0008Detergent materials or soaps characterised by their shape or physical properties aqueous liquid non soap compositions
    • CCHEMISTRY; METALLURGY
    • C11ANIMAL OR VEGETABLE OILS, FATS, FATTY SUBSTANCES OR WAXES; FATTY ACIDS THEREFROM; DETERGENTS; CANDLES
    • C11DDETERGENT COMPOSITIONS; USE OF SINGLE SUBSTANCES AS DETERGENTS; SOAP OR SOAP-MAKING; RESIN SOAPS; RECOVERY OF GLYCEROL
    • C11D3/00Other compounding ingredients of detergent compositions covered in group C11D1/00
    • C11D3/16Organic compounds
    • C11D3/20Organic compounds containing oxygen
    • C11D3/2072Aldehydes-ketones
    • CCHEMISTRY; METALLURGY
    • C11ANIMAL OR VEGETABLE OILS, FATS, FATTY SUBSTANCES OR WAXES; FATTY ACIDS THEREFROM; DETERGENTS; CANDLES
    • C11DDETERGENT COMPOSITIONS; USE OF SINGLE SUBSTANCES AS DETERGENTS; SOAP OR SOAP-MAKING; RESIN SOAPS; RECOVERY OF GLYCEROL
    • C11D3/00Other compounding ingredients of detergent compositions covered in group C11D1/00
    • C11D3/16Organic compounds
    • C11D3/20Organic compounds containing oxygen
    • C11D3/2075Carboxylic acids-salts thereof
    • C11D3/2079Monocarboxylic acids-salts thereof
    • CCHEMISTRY; METALLURGY
    • C11ANIMAL OR VEGETABLE OILS, FATS, FATTY SUBSTANCES OR WAXES; FATTY ACIDS THEREFROM; DETERGENTS; CANDLES
    • C11DDETERGENT COMPOSITIONS; USE OF SINGLE SUBSTANCES AS DETERGENTS; SOAP OR SOAP-MAKING; RESIN SOAPS; RECOVERY OF GLYCEROL
    • C11D3/00Other compounding ingredients of detergent compositions covered in group C11D1/00
    • C11D3/16Organic compounds
    • C11D3/26Organic compounds containing nitrogen
    • C11D3/32Amides; Substituted amides
    • CCHEMISTRY; METALLURGY
    • C11ANIMAL OR VEGETABLE OILS, FATS, FATTY SUBSTANCES OR WAXES; FATTY ACIDS THEREFROM; DETERGENTS; CANDLES
    • C11DDETERGENT COMPOSITIONS; USE OF SINGLE SUBSTANCES AS DETERGENTS; SOAP OR SOAP-MAKING; RESIN SOAPS; RECOVERY OF GLYCEROL
    • C11D3/00Other compounding ingredients of detergent compositions covered in group C11D1/00
    • C11D3/16Organic compounds
    • C11D3/34Organic compounds containing sulfur
    • C11D3/3409Alkyl -, alkenyl -, cycloalkyl - or terpene sulfates or sulfonates
    • CCHEMISTRY; METALLURGY
    • C11ANIMAL OR VEGETABLE OILS, FATS, FATTY SUBSTANCES OR WAXES; FATTY ACIDS THEREFROM; DETERGENTS; CANDLES
    • C11DDETERGENT COMPOSITIONS; USE OF SINGLE SUBSTANCES AS DETERGENTS; SOAP OR SOAP-MAKING; RESIN SOAPS; RECOVERY OF GLYCEROL
    • C11D3/00Other compounding ingredients of detergent compositions covered in group C11D1/00
    • C11D3/16Organic compounds
    • C11D3/34Organic compounds containing sulfur
    • C11D3/3418Toluene -, xylene -, cumene -, benzene - or naphthalene sulfonates or sulfates
    • CCHEMISTRY; METALLURGY
    • C11ANIMAL OR VEGETABLE OILS, FATS, FATTY SUBSTANCES OR WAXES; FATTY ACIDS THEREFROM; DETERGENTS; CANDLES
    • C11DDETERGENT COMPOSITIONS; USE OF SINGLE SUBSTANCES AS DETERGENTS; SOAP OR SOAP-MAKING; RESIN SOAPS; RECOVERY OF GLYCEROL
    • C11D3/00Other compounding ingredients of detergent compositions covered in group C11D1/00
    • C11D3/16Organic compounds
    • C11D3/36Organic compounds containing phosphorus
    • CCHEMISTRY; METALLURGY
    • C11ANIMAL OR VEGETABLE OILS, FATS, FATTY SUBSTANCES OR WAXES; FATTY ACIDS THEREFROM; DETERGENTS; CANDLES
    • C11DDETERGENT COMPOSITIONS; USE OF SINGLE SUBSTANCES AS DETERGENTS; SOAP OR SOAP-MAKING; RESIN SOAPS; RECOVERY OF GLYCEROL
    • C11D3/00Other compounding ingredients of detergent compositions covered in group C11D1/00
    • C11D3/16Organic compounds
    • C11D3/36Organic compounds containing phosphorus
    • C11D3/362Phosphates or phosphites
    • CCHEMISTRY; METALLURGY
    • C11ANIMAL OR VEGETABLE OILS, FATS, FATTY SUBSTANCES OR WAXES; FATTY ACIDS THEREFROM; DETERGENTS; CANDLES
    • C11DDETERGENT COMPOSITIONS; USE OF SINGLE SUBSTANCES AS DETERGENTS; SOAP OR SOAP-MAKING; RESIN SOAPS; RECOVERY OF GLYCEROL
    • C11D3/00Other compounding ingredients of detergent compositions covered in group C11D1/00
    • C11D3/43Solvents

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Wood Science & Technology (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Emergency Medicine (AREA)
  • Physics & Mathematics (AREA)
  • General Engineering & Computer Science (AREA)
  • High Energy & Nuclear Physics (AREA)
  • Detergent Compositions (AREA)

Abstract

The invention provides a radioactive decontamination foam-based eutectic solvent, a preparation method and application thereof, wherein the eutectic solvent comprises a hydrogen bond donor and a hydrogen bond acceptor; the hydrogen bond donor is an acidic compound with a specific substituent, the hydrogen bond acceptor is an oxygen coordination neutral compound with a specific substituent, and the specific substituent is a symmetrical or asymmetrical straight-chain alkyl, branched-chain alkyl, cycloalkyl or aryl with 1-16C atoms. The foam-based eutectic solvent of the invention can realize high-efficiency decontamination of various radionuclides under a broad-spectrum condition.

Description

Radioactive decontamination foam-based eutectic solvent and preparation method and application thereof
Technical Field
The invention belongs to the technical fields of nuclear facility retirement, nuclear waste treatment and disposal, and relates to a radioactive decontamination foam-based eutectic solvent, a preparation method and application thereof.
Background
Nuclear energy is a strategic energy source with continuous stability, cleanliness and high energy density, and the development of the nuclear energy source has important significance for energy safety guarantee. However, nuclear fuel and spent fuel formed after use are radioactive, and leakage can cause great harm to the natural environment. In order to ensure ecological health development and safe utilization of nuclear energy, it is necessary to perform effective decontamination treatment on radioactive contaminated equipment during retirement of nuclear facilities. In recent years, a large number of nuclear reactors in various countries of the world enter retirement, resulting in a large increase in the demand for radioactive decontamination work in the nuclear power industry.
Radioactive decontamination mainly comprises methods of mechanical decontamination, chemical decontamination, physical decontamination and the like. The chemical decontamination is to remove the radionuclide on the surface by utilizing the actions of dissolution, oxidation reduction, complexation, passivation, surface infiltration and the like of chemical reagents, has various irreplaceable advantages, and is widely applied in decontamination industry. Chemical decontamination products consist essentially of a carrier and a decontamination active ingredient. Wherein, the carrier can contain or carry the decontamination active ingredient, support and assist decontamination. Common carriers mainly comprise foam, film body and the like, and various commercial products are available at present. The detergent active ingredients are combined with radionuclides through chemical action, are usually prepared by mixing complexing agents, redox agents and the like, and are the key content of the research and development of various detergents currently. Because the radiation dose of spent fuel is extremely high and the nuclides with long-term radioactivity are numerous, the high requirements on decontamination active ingredients are put forward in the aspects of decontamination efficiency, decontamination nuclide types and the like. The development of novel highly effective and broad spectrum detergent actives is a key tool to the decommissioning of nuclear facilities.
Disclosure of Invention
Aiming at the defects of the prior art, the invention aims to provide a radioactive decontamination foam-based eutectic solvent, and a preparation method and application thereof. The foam-based eutectic solvent of the invention can realize high-efficiency decontamination of various radionuclides under a broad-spectrum condition.
To achieve the purpose, the invention adopts the following technical scheme:
In one aspect, the present invention provides a radioactive detersive foam-based eutectic solvent comprising a eutectic solvent and a foam carrier, the eutectic solvent comprising a hydrogen bond donor and a hydrogen bond acceptor; the hydrogen bond donor is an acidic compound having a specific substituent, and the hydrogen bond acceptor is an oxygen coordination neutral compound having a specific substituent, and the specific substituent is a symmetrical or asymmetrical linear alkyl, branched alkyl, cycloalkyl or aryl group having 1 to 16 (e.g., 1,2, 4, 6, 8, 10, 12, 14 or 16) C atoms.
The eutectic solvent of the present invention is a two-component or three-component eutectic mixture of a combination of hydrogen bond acceptors and hydrogen bond donors. Because the hydrogen bond donor/hydrogen bond acceptor molecules are selected and combined in a very rich way, the combination of a plurality of nuclides is hopefully realized through the targeted design of the eutectic solvent, and the efficient decontamination of radioactive pollution nuclear facilities is further promoted.
Preferably, the hydrogen bond donor is selected from any one or a combination of at least two of phosphonic acid, dithiophosphinic acid, organic carboxylic acid, organic sulfonic acid or organic sulfinic acid.
In the present invention, the hydrogen bond donor has the following structural formula:
r may be a symmetrical or asymmetrical straight chain alkyl, branched alkyl, cycloalkyl or aryl group having 1 to 16C atoms.
Preferably, the hydrogen bond donor is selected from any one or a combination of at least two of bis (2-ethylhexyl) phosphonic acid, bis (2, 4-trimethylpentyl) dithiophosphinic acid, n-decanoic acid, phenylsulfonic acid or cyclohexylsulfinic acid.
Preferably, the hydrogen bond acceptor is selected from any one or a combination of at least two of ketone, amide clamp ether, neutral phosphines or phosphate ligands.
In the present invention, the hydrogen bond acceptor has the following structural formula:
r may be a symmetrical or asymmetrical straight chain alkyl, branched alkyl, cycloalkyl or aryl group having 1 to 16C atoms.
Preferably, the hydrogen bond acceptor is selected from any one or a combination of at least two of tetra-N-octyl diamide clip ether, methyl butyl ketone, N-dibutyl-hexadecyl monoamide, trioctylphosphine oxide or tributyl phosphate.
Preferably, the molar ratio of the hydrogen bond donor to the hydrogen bond acceptor may be in the range of 1:10 to 10:1, for example 1:10, 1:9, 1:8, 1:7, 1:6, 1:5, 1:4, 1:3, 1:2, 1:1, 2:1, 3:1, 4:1, 5:1, 6:1, 7:1, 8:1, 9:1 or 10:1.
Preferably, the foam carrier is formed by mixing a surfactant with water.
In the present invention, the surfactant may be an anionic surfactant, a cationic surfactant, an amphoteric surfactant, or a nonionic surfactant.
Preferably, the volume ratio of surfactant to water may be 1:10-10:1, for example 1:10, 1:9, 1:8, 1:7, 1:6, 1:5, 1:4, 1:3, 1:2, 1:1, 2:1, 3:1, 4:1, 5:1, 6:1, 7:1, 8:1, 9:1 or 10:1.
Preferably, the volume ratio of eutectic solvent to foam carrier is 1:10-10:1, e.g., 1:10, 1:9, 1:8, 1:7, 1:6, 1:5, 1:4, 1:3, 1:2, 1:1, 2:1, 3:1, 4:1, 5:1, 6:1, 7:1, 8:1, 9:1, or 10:1.
In another aspect, the present invention provides a method for preparing the radioactive decontamination foam-based eutectic solvent as described above, the method comprising the steps of:
(1) Mixing a hydrogen bond donor and a hydrogen bond acceptor to obtain a eutectic solvent which is used as a radioactive decontamination active ingredient;
(2) And mixing the eutectic solvent with a foam carrier to obtain the radioactive decontamination foam-based eutectic solvent.
In another aspect, the present invention provides the use of a radiodecontaminating foam-based eutectic solvent as described above as a radionuclide decontaminant.
Preferably, the application is spraying the radioactive decontamination foam-based eutectic solvent on the radioactive contamination surface, and wiping the surface after standing, so that efficient decontamination of various radionuclides under a broad spectrum of conditions can be realized.
Preferably, the rest time may be 1-60 minutes, for example 1 minute, 5 minutes, 10 minutes, 15 minutes, 20 minutes, 25 minutes, 30 minutes, 35 minutes, 40 minutes, 45 minutes, 50 minutes, 55 minutes or 60 minutes.
Preferably, the material of the contaminated surface can be stainless steel, aluminum, wood or high polymer material.
Preferably, the acidity of the contaminated surface may be any acidity in the range of pH 14-pH 1 (e.g., pH14, 13, 12, 11, 10, 9, 8, 7, 6, 5, 4, 3, 2, or 1) and 0.1-14mol/L (e.g., 0.1mol/L, 0.5mol/L, 1mol/L, 3mol/L, 5mol/L, 8mol/L, 10mol/L, 12mol/L, or 14 mol/L) H +.
Preferably, the wiping material used for the wiping surface can be paper, cotton or synthetic fiber.
Preferably, the radionuclide is a radionuclide of valency I-VII.
Preferably, the radionuclide is one or a combination of at least two of cesium (Cs (I)), strontium (Sr (II)), americium (Am (III)), curium (Cm (III)), lanthanide (Ln (III)), thorium (Th (IV)), plutonium (Pu (IV)), neptunium (Np (V)), uranium (U (VI)) or technetium (Tc (VII)).
Compared with the prior art, the invention has the following beneficial effects:
The foam-based eutectic solvent is used as a detergent, promotes dissociation of hydrogen ions of acidic compounds through hydrogen bonding, and can realize efficient decontamination of radionuclides in all acidity ranges. The eutectic solvent as an active ingredient of the detergent is composed of two or more organic ligands, so that synchronous decontamination of various radionuclides under a broad spectrum of conditions can be achieved.
Detailed Description
The technical scheme of the invention is further described by the following specific embodiments. It will be apparent to those skilled in the art that the examples are merely to aid in understanding the invention and are not to be construed as a specific limitation thereof.
The experimental methods described in the following examples are all conventional methods unless otherwise specified; the reagents and materials, unless otherwise specified, are commercially available.
Example 1:
The molar ratio was set to 1:1 with di (2-ethylhexyl) phosphoric acid, and preparing the tetra-n-octyl diamide clamp ether-di (2-ethylhexyl) phosphoric acid eutectic solvent by a heating-cooling method. The anionic surfactant sodium octoate was mixed with water according to 1:1 by volume ratio to form a foam carrier. Mixing the eutectic solvent and the foam carrier according to the following ratio of 1:1 to prepare the foam-based eutectic solvent type radioactive detergent 1. Detergent 1 was sprayed on a stainless steel surface contaminated with Cs (I) at pH 3 and allowed to stand for 10 minutes. The surface was then wiped with paper and the surface was tested for a soil release rate of 95%.
Example 2:
The molar ratio was set to 1:1 with di (2-ethylhexyl) phosphonic acid, and preparing the tetra-n-octyl diamide clamp ether-di (2-ethylhexyl) phosphonic acid eutectic solvent by a heating-cooling method. The anionic surfactant sodium octoate was mixed with water according to 1:1 by volume ratio to form a foam carrier. Mixing the eutectic solvent and the foam carrier according to the following ratio of 1:1 to prepare the foam-based eutectic solvent type radioactive detergent 2. Detergent 2 was sprayed on a stainless steel surface contaminated with Sr (II) at pH 1 and allowed to stand for 10 minutes. The surface was then wiped with paper and the surface was tested for a soil release rate of 98%.
Example 3:
The molar ratio was set to 1:5, mixing methyl butyl ketone and di (2, 4-trimethyl amyl) dithiophosphinic acid, and preparing the methyl butyl ketone-di (2, 4-trimethyl amyl) dithiophosphinic acid eutectic solvent by a dissolution-evaporation method. Mixing the isooctylamine hydrochloride serving as a cationic surfactant with water according to the following formula 1:5 by volume ratio to form a foam carrier. Mixing the eutectic solvent and the foam carrier according to the following ratio of 1:5, and preparing the foam-based eutectic solvent type radioactive detergent 3. Detergent 3 was sprayed on an aluminum material surface having a pH of 14 and contaminated with Am (III), and allowed to stand for 1 minute. The surface was then wiped with cotton cloth and the surface soil release rate tested reached 99%.
Example 4:
The molar ratio was set to 1:10, N-dibutyl-hexadecyl monoamide is mixed with N-capric acid, and the N, N-dibutyl-hexadecyl monoamide-N-capric acid eutectic solvent is prepared by an ultrasonic method. The amphoteric surfactant amino acid is mixed with water according to a ratio of 1:10 by volume, to form a foam carrier. Mixing the eutectic solvent and the foam carrier according to the following ratio of 1:10 by volume ratio to prepare the foam-based eutectic solvent type radioactive detergent 4. Detergent 4 was sprayed on the woody surface at pH 5 and contaminated with Cm (III) and allowed to stand for 30 minutes. And then the surface is wiped by adopting synthetic fiber, and the decontamination rate of the tested surface reaches 99 percent.
Example 5:
The molar ratio was set to 5:1 with phenylsulfonic acid, and preparing the trioctylphosphine oxide-phenylsulfonic acid eutectic solvent by a heating-cooling method. Mixing the nonionic surfactant glycerol and water according to a ratio of 5:1 by volume ratio to form a foam carrier. Mixing the eutectic solvent and the foam carrier according to a ratio of 5:1, and preparing the foam-based eutectic solvent type radioactive detergent 5. Spraying the detergent 5 on the surface of the high polymer material which is 1mol/LH + and is polluted by Ln (III), and standing for 60 minutes. The surface was then wiped with paper and the surface was tested for a soil release rate of 99%.
Example 6:
The molar ratio was set to 10:1 is mixed with the cyclohexylsulfinic acid, and the tributyl phosphate-cyclohexylsulfinic acid eutectic solvent is prepared by a heating-cooling method. The anionic surfactant sodium octoate is mixed with water according to a ratio of 10:1 by volume ratio to form a foam carrier. Mixing the eutectic solvent and a foam carrier according to a ratio of 10:1, and preparing the foam-based eutectic solvent type radioactive detergent 6. Detergent 6 was sprayed on a stainless steel surface contaminated with Th (IV) at 5mol/L H + and allowed to stand for 10 minutes. The surface was then wiped with paper and the surface soil release rate tested reached 100%.
Example 7:
The molar ratio was set to 1:1 with di (2-ethylhexyl) phosphoric acid, and preparing the tetra-n-octyl diamide clamp ether-di (2-ethylhexyl) phosphoric acid eutectic solvent by a heating-cooling method. The anionic surfactant sodium octoate was mixed with water according to 1:1 by volume ratio to form a foam carrier. Mixing the eutectic solvent and the foam carrier according to the following ratio of 1:1, and preparing the foam-based eutectic solvent type radioactive detergent 7. Detergent 7 was sprayed onto a stainless steel surface contaminated with Pu (IV) at 14mol/L H + and allowed to stand for 10 minutes. The surface was then wiped with paper and the surface soil release rate tested reached 100%.
Example 8:
The molar ratio was set to 1:1 with di (2-ethylhexyl) phosphoric acid, and preparing the tetra-n-octyl diamide clamp ether-di (2-ethylhexyl) phosphoric acid eutectic solvent by a heating-cooling method. The anionic surfactant sodium octoate was mixed with water according to 1:1 by volume ratio to form a foam carrier. Mixing the eutectic solvent and the foam carrier according to the following ratio of 1:1, and preparing the foam-based eutectic solvent type radioactive detergent 8. Detergent 8 was sprayed on a stainless steel surface contaminated with Np (V) at pH 1 and allowed to stand for 10 minutes. The surface was then wiped with paper and the surface soil release rate tested reached 77%.
Example 9:
The molar ratio was set to 1:1 with di (2-ethylhexyl) phosphoric acid, and preparing the tetra-n-octyl diamide clamp ether-di (2-ethylhexyl) phosphoric acid eutectic solvent by a heating-cooling method. The anionic surfactant sodium octoate was mixed with water according to 1:1 by volume ratio to form a foam carrier. Mixing the eutectic solvent and the foam carrier according to the following ratio of 1:1, and preparing the foam-based eutectic solvent type radioactive detergent 9. Detergent 9 was sprayed on the stainless steel surface contaminated with U (VI) at pH 1 and allowed to stand for 10 minutes. The surface was then wiped with paper and the surface soil release rate tested reached 100%.
Example 10:
The molar ratio was set to 1:1 with di (2-ethylhexyl) phosphoric acid, and preparing the tetra-n-octyl diamide clamp ether-di (2-ethylhexyl) phosphoric acid eutectic solvent by a heating-cooling method. The anionic surfactant sodium octoate was mixed with water according to 1:1 by volume ratio to form a foam carrier. Mixing the eutectic solvent and the foam carrier according to the following ratio of 1:1, and preparing the foam-based eutectic solvent type radioactive detergent 10. The detergent 10 was sprayed on a stainless steel surface having a pH of 1 and contaminated with Tc (VII), and allowed to stand for 10 minutes. The surface was then wiped with paper and the surface was tested for a soil release rate of 97%.
Comparative example 1:
the anionic surfactant sodium octoate was mixed with water according to 1:1 by volume, and forming foam. The foam was sprayed onto a stainless steel surface at pH 3 and contaminated with Cs (I) and allowed to stand for 10 minutes. The surface was then wiped with paper and the surface was tested for a soil release rate of 7%.
Comparative example 2:
The anionic surfactant sodium octoate was mixed with water according to 1:1 by volume, and forming foam. The foam was sprayed onto a stainless steel surface having a pH of 1 and being contaminated with Sr (II), and allowed to stand for 10 minutes. The surface was then wiped with paper and the surface was tested for a soil release rate of 12%.
Comparative example 3:
mixing the isooctylamine hydrochloride serving as a cationic surfactant with water according to the following formula 1:5 by volume, and forming foam. The foam was sprayed onto an aluminum surface of pH 14 and contaminated with Am (III) and allowed to stand for 1 minute. The surface was then rubbed with cotton cloth and the surface soil release rate was tested to 23%.
Comparative example 4:
The amphoteric surfactant amino acid is mixed with water according to a ratio of 1:10 by volume, and forming a foam. Foam was sprayed on the wood surface at pH 5 and contaminated with Cm (III) and allowed to stand for 30 minutes. The surface was then wiped with synthetic fibers and the surface was tested for soil release up to 24%.
Comparative example 5:
mixing the nonionic surfactant glycerol and water according to a ratio of 5:1 by volume, and forming foam. Spraying the foam on the surface of the high polymer material which is 1mol/L H + and polluted by Ln (III), and standing for 60 minutes. The surface was then wiped with paper and the surface was tested for a soil release rate of 20%.
Comparative example 6:
The anionic surfactant sodium octoate is mixed with water according to a ratio of 10:1 by volume, and forming foam. The foam was sprayed on a stainless steel surface contaminated with Th (IV) at 5mol/L H + and allowed to stand for 10 minutes. The surface was then wiped with paper and the surface soil release rate tested reached 32%.
Comparative example 7:
The anionic surfactant sodium octoate was mixed with water according to 1:1 by volume, and forming foam. The foam was sprayed onto a stainless steel surface of 14mol/L H + and contaminated with Pu (IV) and allowed to stand for 10 minutes. The surface was then wiped with paper and the surface soil release rate tested reached 33%.
Comparative example 8:
The anionic surfactant sodium octoate was mixed with water according to 1:1 by volume, and forming foam. Foam was sprayed on a stainless steel surface having a pH of 1 and contaminated with Np (V) and allowed to stand for 10 minutes. The surface was then wiped with paper and the surface was tested for a soil release rate of 11%.
Comparative example 9:
The anionic surfactant sodium octoate was mixed with water according to 1:1 by volume, and forming foam. The foam was sprayed onto a stainless steel surface having a pH of 1 and contaminated with U (VI) and allowed to stand for 10 minutes. The surface was then wiped with paper and the surface soil release rate tested reached 22%.
Comparative example 10:
The anionic surfactant sodium octoate was mixed with water according to 1:1 by volume, and forming foam. The foam was sprayed onto a stainless steel surface having a pH of 1 and contaminated with Tc (VII) and allowed to stand for 10 minutes. The surface was then wiped with paper and the surface soil release rate tested reached 23%.
Table 1 comparison of detergent and foam stain removal effect
The applicant states that the present invention is illustrated by the above examples as well as the method of preparing and using the same, but the invention is not limited to, i.e. it is not meant that the invention must be practiced in dependence upon the above examples. It should be apparent to those skilled in the art that any modification of the present invention, equivalent substitution of raw materials for the product of the present invention, addition of auxiliary components, selection of specific modes, etc., falls within the scope of the present invention and the scope of disclosure.

Claims (10)

1. A radioactive decontamination foam-based eutectic solvent, wherein the radioactive decontamination foam-based eutectic solvent comprises a eutectic solvent and a foam carrier, the eutectic solvent comprising a hydrogen bond donor and a hydrogen bond acceptor; the hydrogen bond donor is an acidic compound with a specific substituent, the hydrogen bond acceptor is an oxygen coordination neutral compound with a specific substituent, and the specific substituent is a symmetrical or asymmetrical straight-chain alkyl, branched-chain alkyl, cycloalkyl or aryl with 1-16C atoms.
2. The radiodecontaminating foam-based eutectic solvent of claim 1, wherein the hydrogen bond donor is selected from any one or a combination of at least two of phosphonic acid, dithiophosphinic acid, organic carboxylic acid, organic sulfonic acid, or organic sulfinic acid.
3. The radiodecontaminating foam-based eutectic solvent of claim 1 or 2, wherein the hydrogen bond donor is selected from any one or a combination of at least two of bis (2-ethylhexyl) phosphonic acid, bis (2, 4-trimethylpentyl) dithiophosphinic acid, n-decanoic acid, phenylsulfonic acid, or cyclohexylsulfinic acid.
4. A radiodecontamination foam-based eutectic solvent according to any one of claims 1-3, wherein the hydrogen bond acceptors are selected from any one or a combination of at least two of ketones, amides, amide clamp ethers, neutral phosphines or phosphate ligands;
preferably, the hydrogen bond acceptor is selected from any one or a combination of at least two of tetra-N-octyl diamide clip ether, methyl butyl ketone, N-dibutyl-hexadecyl monoamide, trioctylphosphine oxide or tributyl phosphate.
5. The radiodecontaminating foam-based eutectic solvent of any of claims 1-4, wherein the molar ratio of hydrogen bond donor to hydrogen bond acceptor can be in the range of 1:10-10:1.
6. The radiodecontamination foam-based eutectic solvent of any one of claims 1-5, wherein the foam carrier is formed from a surfactant mixed with water;
Preferably, the surfactant may be an anionic surfactant, a cationic surfactant, an amphoteric surfactant or a nonionic surfactant;
preferably, the volume ratio of the surfactant to water may be in the range 1:10 to 10:1.
7. The radiodecontaminating foam-based eutectic solvent of any of claims 1-6, wherein the volume ratio of the eutectic solvent to foam carrier is 1:10-10:1.
8. The method of preparing a radioactively decontaminating foam-based eutectic solvent according to any of claims 1-7, comprising the steps of:
(1) Mixing a hydrogen bond donor and a hydrogen bond acceptor to obtain a eutectic solvent which is used as a radioactive decontamination active ingredient;
(2) And mixing the eutectic solvent with a foam carrier to obtain the radioactive decontamination foam-based eutectic solvent.
9. Use of the radiodecontaminating foam-based eutectic solvent according to any of claims 1-7 as a radionuclide decontaminant.
10. The use according to claim 9, wherein the use is to spray the radioactive decontamination foam-based eutectic solvent onto the radioactive contaminated surface, and to wipe the surface after standing;
preferably, the rest time may be 1 to 60 minutes;
preferably, the material of the polluted surface can be stainless steel, aluminum, wood or high polymer material;
Preferably, the acidity of the contaminated surface may be any acidity in the range of pH 14-pH 1 and 0.1-14mol/L H +;
Preferably, the material of the wiper used for wiping the surface can be paper, cotton or synthetic fiber;
preferably, the radionuclide is a radionuclide of valency I-VII;
preferably, the radionuclide is one or a combination of at least two of cesium, strontium, americium, curium, lanthanide, thorium, plutonium, neptunium, uranium or technetium.
CN202410148804.XA 2024-02-02 2024-02-02 Radioactive decontamination foam-based eutectic solvent and preparation method and application thereof Pending CN117987211A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202410148804.XA CN117987211A (en) 2024-02-02 2024-02-02 Radioactive decontamination foam-based eutectic solvent and preparation method and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202410148804.XA CN117987211A (en) 2024-02-02 2024-02-02 Radioactive decontamination foam-based eutectic solvent and preparation method and application thereof

Publications (1)

Publication Number Publication Date
CN117987211A true CN117987211A (en) 2024-05-07

Family

ID=90894884

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202410148804.XA Pending CN117987211A (en) 2024-02-02 2024-02-02 Radioactive decontamination foam-based eutectic solvent and preparation method and application thereof

Country Status (1)

Country Link
CN (1) CN117987211A (en)

Similar Documents

Publication Publication Date Title
Madic et al. Separation of long-lived radionuclides from high active nuclear waste
JPH0145600B2 (en)
JP2012518165A (en) Method for decontamination of radioactively contaminated surfaces
CN115322840B (en) Radioactive contamination decontaminating liquid and its preparation and application
JPH02229900A (en) Woven fabric rinsing composition for removing surface active agent residue
CN102773067B (en) Preparation method of selective adsorbent for magnetic cesium
KR20140095266A (en) Chelate free chemical decontamination reagent for removal of the dense radioactive oxide layer on the metal surface and chemical decontamination method using the same
CN113563980A (en) Uranium radioactive decontaminant and uranium removing method of uranium-containing device
Chmielewski et al. Radiation chemistry for modern nuclear energy development
CN117987211A (en) Radioactive decontamination foam-based eutectic solvent and preparation method and application thereof
KR830002521B1 (en) Decontamination composition suitable for radioactive device
CA1230806A (en) Ceric acid decontamination of nuclear reactors
CN109504561A (en) It is a kind of for removing the cleaning agent of body surface radioactive pollution
KR102295937B1 (en) Ambient temperature decontamination of nuclear power plant component surfaces containing radionuclides in a metal oxide
KR102633134B1 (en) Treatment Method of Radioactive Waste Containing Chemical Complexing Agents
US4880559A (en) Ceric acid decontamination of nuclear reactors
RU2080666C1 (en) Method for processing of active nitrate raffinates produced by regeneration of nuclear fuel
KR101601201B1 (en) Chelate free chemical decontamination reagent for removal of the dense radioactive oxide layer on the metal surface and chemical decontamination method using the same
JPS60149594A (en) Homogeneous liquid mixture for liquid scintillation count analysis
KR100679562B1 (en) A removal of radioactive contaminant
US5678232A (en) Lead decontamination method
RU2457560C1 (en) Method of chemical decontamination of radioactive materials
Kádár et al. Accumulation of uranium, transuranium and fission products on stainless steel surfaces. I. A comprehensive view of the experimental parameters influencing the extent and character of the contamination
Werme et al. Radiolytically induced oxidative dissolution of spent nuclear fuel
Guilbert et al. Radiolytic oxidation of iodine in the containment at high temperature and dose rate

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