CN115322840A - Radioactive contamination decontamination solution and preparation and application thereof - Google Patents

Radioactive contamination decontamination solution and preparation and application thereof Download PDF

Info

Publication number
CN115322840A
CN115322840A CN202210948569.5A CN202210948569A CN115322840A CN 115322840 A CN115322840 A CN 115322840A CN 202210948569 A CN202210948569 A CN 202210948569A CN 115322840 A CN115322840 A CN 115322840A
Authority
CN
China
Prior art keywords
parts
acid
group
sodium
decontamination
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
CN202210948569.5A
Other languages
Chinese (zh)
Inventor
王明望
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.)
Changsha Chengde Huanyu Technology Co ltd
Original Assignee
Changsha Chengde Huanyu Technology 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 Changsha Chengde Huanyu Technology Co ltd filed Critical Changsha Chengde Huanyu Technology Co ltd
Priority to CN202210948569.5A priority Critical patent/CN115322840A/en
Publication of CN115322840A publication Critical patent/CN115322840A/en
Pending legal-status Critical Current

Links

Classifications

    • 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
    • C11D1/66Non-ionic compounds
    • 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
    • C11D3/02Inorganic compounds ; Elemental compounds
    • C11D3/04Water-soluble compounds
    • C11D3/042Acids
    • 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
    • C11D3/02Inorganic compounds ; Elemental compounds
    • C11D3/04Water-soluble compounds
    • C11D3/06Phosphates, including polyphosphates
    • 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
    • C11D3/2003Alcohols; Phenols
    • C11D3/2065Polyhydric alcohols
    • 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
    • C11D3/2086Hydroxy carboxylic 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
    • C11D3/20Organic compounds containing oxygen
    • C11D3/22Carbohydrates or derivatives thereof
    • C11D3/222Natural or synthetic polysaccharides, e.g. cellulose, starch, gum, alginic acid or cyclodextrin
    • 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
    • C11D3/33Amino carboxylic acids
    • 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
    • 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
    • G21F9/001Decontamination of contaminated objects, apparatus, clothes, food; Preventing contamination thereof

Landscapes

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

Abstract

The invention belongs to the field of decontamination solutions, and particularly discloses a radioactive contamination decontamination solution and preparation and application thereof, wherein the radioactive contamination decontamination solution consists of a chelating agent A group, an organic solvent B group, a regulator C group and an auxiliary agent D group; based on 100 parts by weight: the group A chelating agents include: 3-6 parts of hydroxyethylidene diphosphonic acid, 8-12 parts of pentasodium diethyltriaminepentaacetate, 2-8 parts of sodium hexametaphosphate, 3-6 parts of sodium pyrophosphate and 3-6 parts of disodium ethylene diamine tetraacetate; the organic solvent B group comprises: 3-5 parts of acetylacetone, 2-4 parts of glycine and 0.1-1 part of water-soluble chitosan; the group C modulators include: 3-6 parts of boric acid, 1-3 parts of citric acid and 4-10 parts of coconut diethanolamide; the auxiliary agent group D comprises: 3-6 parts of glycerol; the balance being water. The decontamination solution disclosed by the invention has the advantages of high decontamination efficiency, small corrosivity, multiple application scenes, multiple types of radioactive nuclides capable of decontamination and wide application range, and can be applied to the surface of human skin, indoor environment and instruments and meters.

Description

Radioactive contamination decontamination solution and preparation and application thereof
Technical Field
The invention belongs to the field of decontamination solutions, and particularly discloses a radioactive contamination decontamination solution and preparation and application thereof.
Background
The radioactive contamination is that radioactive substances generated in nuclear radiation and nuclear explosion accidents are contaminated to surrounding personnel, equipment, animals, plants and environments, wherein the radioactive substances mainly comprise nuclear fission products, induced radioactive substances and non-fission nuclear charges; the main ways of causing staining are:
(1) The radioactive falling ash is settled in the air in a settling mode, is deposited on the ground, is adhered to the surfaces of human bodies and objects, and is suspended in the air and water, so that the environment is polluted and the like;
(2) Some elements in the environment are made radioactive in such a way that induced radioactivity is generated, causing internal contamination.
The radioactive contamination elimination is a washing and eliminating action for eliminating radioactive contamination of an infected object or reducing the contamination degree of the infected object, and comprises washing, wiping, flapping, sweeping, masking, filtering, curing and transferring and the like, and no matter chemical elimination or physical elimination, the structure, the composition and the property of atomic nuclei cannot be changed, namely the inherent attenuation law cannot be changed, the radioactivity of the atomic nuclei cannot be eliminated, in order to reduce the radioactive hazard of radioactive substances and reduce the contact danger, the only method is to remove the radioactive substances from the polluted surface, and the elimination degree mainly depends on the contamination characteristics of the radioactive substances, the used eliminating agent, the eliminating method and the like.
At present, the common radioactive contamination eliminators on the market mainly comprise a surface active eliminator, a chelating eliminator, a redox eliminator, an acid-base eliminator, a strippable film eliminator and a self-brittle eliminator; each has advantages and disadvantages, and the targeted radionuclides are different, and the application scenes are also different;
chinese patent CN111870595A nuclide decontamination solution, and preparation method and application thereof, wherein the nuclide decontamination solution comprises, by weight, 0.3-6% of pentasodium diethylenetriamine pentaacetate, 0.1-5% of an auxiliary chelating agent, and 0.1-up to c2 percent of adsorbent, 0.1 to 2 percent of surfactant, 1 to 10 percent of preservative, 0.1 to 1 percent of defoaming agent, 0.1 to 1 percent of acid-base regulator, 0.1 to 2 percent of stabilizer and the balance of water. The invention belongs to a combination product of a chelate type eliminator and a surface active type eliminator, and has the advantages of high decontamination efficiency, wide application range, strong environmental adaptability and long storage time. But it has problems that the contaminants are only 32 P, the infected object is only pig skin, the experimental process is carried out by a decontamination instrument, the infection time is only 1 minute, the decontamination time is also only 1 minute, the analysis is carried out on the patent right requirements and the experimental reports, 32 the P nuclide is completely different from the actinide or transition metal nuclide in performance, and 32 the P nuclide is particularly small in application, is only used in nuclear medicine, does not have wide application, and is not a representative radionuclide, so that the P nuclide cannot be explained to have a good decontamination effect on actinide nuclides or transition metal nuclides. Is the subject of the infection only pigskin, then in addition to pigskin, does it have an effect on the surrounding environment such as stainless steel, ceramic tiles, plastics, etc.? In the experimental process, the decontamination instrument is used, and then the decontamination instrument is not used in the actual use process, and whether the decontamination effect is the same or not? The reproducibility of the experimental process cannot be completed; the contamination time is only 1 minute, the decontamination time is also only 1 minute, and the contamination is equivalent to the washing with dripping, but in the actual process, the situation can be processed by using a rag, a series of problems such as the situation that the contamination time is very long and the radionuclide permeates below the surface are not solved, the environmental adaptability is strong and the storage time is long are declared, and the data which does not support the decontamination data in the environments such as plateau, rainforest and the like and the stability experiment data under high temperature and low temperature are not provided, so the method is contradictory to the patent authority requirements;
chinese patent CN111269761A decontamination liquid and application thereof in decontamination of actinide nuclide and transition metal nuclide pollution, wherein each 100 weight parts of the decontamination liquid contains 0.8-1.2 parts of 2-hydroxyphosphonoacetic acid, 6-8 parts of nitrilotrimethylene phosphate, 6-8 parts of 2-phosphonic acid butane-1,2,4-tricarboxylic acid, 0.8-1.2 parts of ethylene diamine tetramethylene phosphate and 3-5 parts of hydroxy ethylidene diphosphonic acid. The method is used for decontamination of the pollution of the steel nuclide and the transition metal nuclide, and can be better used for decontamination of the pollution of the steel nuclide and the transition metal nuclide on the skin. However, the method has the problems that the high-concentration phosphorus-containing organic acid has high acidity and can soften the cutin of the skin, and the phosphorus-containing organic acid can be adsorbed on the cutin and the surface of a cell membrane to irreversibly damage the skin; the phosphorus-containing organic acid causes secondary pollution to the environment in the use process, for example, after the stainless steel surface is washed and disinfected, the residual phosphorus-containing organic acid continues to react with the stainless steel surface to cause corrosion, further affecting the overall structure, and causing more serious corrosion to instruments and equipment.
Disclosure of Invention
In order to solve the problems, the invention discloses a radioactive contamination decontamination solution and preparation and application thereof.
The technical scheme of the invention is as follows:
a radioactive contamination decontamination solution is provided,
consists of a chelating agent A group, an organic solvent B group, a regulator C group and an auxiliary agent D group;
based on 100 parts by weight:
the group A chelating agents include: 3-6 parts of hydroxyethylidene diphosphonic acid, 8-12 parts of pentasodium diethyltriaminepentaacetate, 2-8 parts of sodium hexametaphosphate, 3-6 parts of sodium pyrophosphate and 3-6 parts of disodium ethylene diamine tetraacetate;
the organic solvent B group comprises: 3-5 parts of acetylacetone, 2-4 parts of glycine and 0.1-1 part of water-soluble chitosan;
the group C modulators include: 3-6 parts of boric acid, 1-3 parts of citric acid and 4-10 parts of coconut diethanolamide;
the auxiliary agent group D comprises: 3-6 parts of glycerol;
the balance being water.
Further, in the radioactive contamination decontamination solution, the hydroxyethylidene diphosphonic acid is replaced by one of amino trimethylene phosphonic acid, ethylene diamine tetramethylene phosphonic acid, sodium hydroxyethylidene diphosphonate, polyamino polyether methylene phosphonic acid, diethylene triamine pentamethylene phosphonic acid and 2-phosphonic butane-1,2,4-tricarboxylic acid.
Further, in the radioactive contamination decontamination solution, the diethyltriamine pentaacetic acid pentasodium is replaced by one of itaconic acid, diethylenetriamine pentaacetic acid trisodium calcium and polyethyleneimine.
Further, in the radioactive contamination decontamination solution, the sodium hexametaphosphate is replaced by one of sodium pyrophosphate, sodium tripolyphosphate and sodium dihydrogen phosphate.
Further, in the radioactive contamination decontamination solution, the disodium ethylene diamine tetraacetate is replaced by one of sodium gluconate and ethylene diamine tetraacetate.
Further, in the radioactive contamination decontamination solution, the acetylacetone is replaced by one of sodium polyacrylate, polyepoxysuccinic acid (sodium) and benzotriazole (sodium).
Further, in the radioactive contamination decontamination solution, the glycine is replaced by one of polyaspartic acid (sodium) and sodium hyaluronate.
Further, in the radioactive contamination decontamination solution, the water-soluble chitosan is replaced by one of polylactic acid, polyglycolic acid and water-soluble silica gel; the boric acid is replaced by one of sodium borate and borax; the citric acid is replaced by one of tartaric acid, sodium citrate and metaphosphoric acid; the coconut diethanolamide is replaced by one of sodium dodecyl polyoxyethylene ether sulfate, fatty alcohol polyoxyethylene ether, disodium sulfosuccinate monoester, cocamidopropyl betaine and sodium dodecyl benzene sulfonate; the glycerol is replaced by one of polyethylene glycol and butanediol.
Further, the preparation method of the radioactive contamination decontamination solution comprises the following steps:
weighing the raw materials in the formula according to a specific weight for later use, adding all the chelating agent group A into a reaction kettle, adding a proper amount of water, stirring at 3000-9000rpm/min at 45-75 ℃ for 30-90min, adding a part of the auxiliary agent group D, simultaneously adding all the organic solvent group B into a stainless steel barrel, adding a proper amount of water, stirring at 8000-12000rpm/min at 70-90 ℃ for 30-90min, adding a part of the auxiliary agent group D, adding all the regulator group C into a glass cup, adding a proper amount of water, stirring at 6000-10000rpm/min and 45-75 ℃ for 15-45min, adding the organic solvent group B into the reaction kettle, stirring at 4000-8000rpm/min and 45-75 ℃ for 5-15min, adding the regulator group C at 4500-7500rpm/min and stirring at 45-75 ℃ for 5-15min until the solution is transparent.
Preferably, the method comprises the following steps: weighing the raw materials in the formula according to the specific weight for later use, adding all the chelating agent group A into a reaction kettle, adding 50% of water at 6000rpm/min, stirring at 60 ℃ for 60min, adding 50% of the auxiliary agent group D, simultaneously adding all the organic solvent group B into a stainless steel barrel, adding 10% of water at 10000rpm/min, stirring at 80 ℃ for 60min, adding 50% of the auxiliary agent group D, adding all the regulator group C into a glass cup, adding 40% of water at 8000rpm/min, stirring at 60 ℃ for 30min, adding the organic solvent group B, stirring at 6000rpm/min and 60 ℃ for 10min into the reaction kettle, adding the regulator group C at 6000rpm/min, stirring at 60 ℃ for 10min until the solution is transparent.
Further, the radioactive contamination decontamination solution is applied to the removal of contamination caused by actinide radionuclides, lanthanide radionuclides, transition metal radionuclides, nonmetal radionuclides and metal radionuclides.
The invention has the following beneficial effects:
1: the cleaning agent has high decontamination efficiency for actinide radionuclide, lanthanide radionuclide, transition metal radionuclide, nonmetal radionuclide and metal radionuclide, has good adaptability for the surfaces of stainless steel, rubber, cement floors, cotton cloth and skin in different fields, and still has good decontamination effect for the contamination degree in different time;
2: the formula system combines a surface active type, a chelating type and an acid-base type remover, and the surface active type adopts a mild amphoteric surfactant and is mild and non-irritant; the chelating type adopts the combination of an ammonia-carboxyl complexing agent and a phosphorus-based complexing agent, greatly improves the chelating capacity and can face a complex use environment; the whole system adopts an acid system, and has good decontamination effect on stubborn stains which are difficult to dissolve and some radioactive particles; the high molecular compound is adopted, so that the foam is fine and smooth and has long duration, the radioactive nuclide can be wrapped, and the radiation damage of the radioactive nuclide to the skin can be isolated to a certain degree;
3: for a certain amount of polluted areas, only a small amount of decontamination solution is needed to be used, the decontamination requirement can be met, the treated radioactive waste liquid or waste is less, the subsequent radioactive treatment is reduced, the operation in the use process is simple, the use is convenient, a special decontamination instrument is not needed, the effective decontamination can be realized only by using common tools in daily life, and radioactive accidents are easy to treat;
4: by adopting the dissolution promotion process, the solubility of each component can be effectively increased, the components are coordinated and promoted to achieve the effect of 1+1>2, a stable PH interval is provided for the system, the dissolution time is greatly shortened, and the stability of the system is improved;
5: according to the embodiment of the invention, according to a national standard method, a quotation is combined, an isotope detection method and a radioactive intensity detection method are adopted, the problem of large harm of radioactive nuclides with long half-life period is avoided, the isotope detection method can be used for verifying the decontamination effect of different nuclides, the repeatability of an experiment is conveniently verified, the operation difficulty is reduced, the radioactive treatment after the experiment is reduced, the isotope detection method and the radioactive intensity detection method are combined for mutual verification, the decontamination effect of a decontamination solution is evaluated from two different angles, and the effectiveness and the credibility of an experiment result are improved;
Detailed Description
The technical solutions in the embodiments of the present invention are clearly and completely described below, and it is obvious that the described embodiments are only a part of the embodiments of the present invention, and not all embodiments. All other embodiments, which can be derived by a person skilled in the art from the embodiments given herein without making any creative effort, shall fall within the protection scope of the present invention.
The reagents or instruments used in the examples of the present invention are not indicated by manufacturers, and are all conventional reagent products commercially available.
Example 1
Preparation example
The formula is as follows: every 100 parts by weight of the decontamination solution contains 6 parts of hydroxyethylidene diphosphonic acid, 10 parts of pentasodium diethyltriaminepentaacetate, 4 parts of sodium hexametaphosphate, 3 parts of sodium pyrophosphate, 4 parts of acetylacetone, 3 parts of disodium ethylene diamine tetraacetate, 3 parts of boric acid, 2 parts of glycine, 1 part of citric acid, 0.2 part of water-soluble chitosan, 5 parts of glycerol, 5 parts of coconut diethanolamide and the balance of water.
Preparation: according to the attributes of raw materials in the formula, the raw materials are divided into a chelating agent A group (hydroxyl ethylidene diphosphonic acid, diethyl triaminepentaacetic acid pentasodium, sodium hexametaphosphate, sodium pyrophosphate and ethylene diamine tetraacetic acid disodium), an organic solvent B group (acetylacetone, glycine and water-soluble chitosan), a regulator C group (boric acid, citric acid and coconut oil acid diethanolamide) and an auxiliary agent D group (glycerol); weighing the raw materials in the formula according to the specific weight for later use, adding all the chelating agents A into a reaction kettle, adding 50% of water at 6000rpm/min, stirring at 60 ℃ for 60min, adding 50% of the auxiliaries D, simultaneously adding all the organic solvents B into a stainless steel barrel, adding 10% of water at 10000rpm/min, stirring at 80 ℃ for 60min, adding 50% of the auxiliaries D, adding all the regulators C into a glass cup, adding 40% of water at 8000rpm/min, stirring at 60 ℃ for 30min, adding the organic solvents B, 6000rpm/min, stirring at 60 ℃ for 10min, adding the regulators C, stirring at 60 ℃ for 10min, and stirring at 60 ℃ for 10min until the solution is transparent.
Example 2
Preparation example
The formula is as follows: every 100 weight parts of the decontamination solution contain 3 parts of hydroxyethylidene diphosphonic acid, 8 parts of pentasodium diethyltriaminepentaacetate, 2 parts of sodium hexametaphosphate, 3 parts of sodium pyrophosphate, 3 parts of acetylacetone, 3 parts of disodium ethylene diamine tetraacetate, 3 parts of boric acid, 2 parts of glycine, 1 part of citric acid, 0.1 part of water-soluble chitosan, 3 parts of glycerol, 4 parts of coconut diethanolamide and the balance of water.
Preparation: according to the attributes of raw materials in the formula, the raw materials are divided into a chelating agent A group (hydroxyl ethylidene diphosphonic acid, diethyl triaminepentaacetic acid pentasodium, sodium hexametaphosphate, sodium pyrophosphate and ethylene diamine tetraacetic acid disodium), an organic solvent B group (acetylacetone, glycine and water-soluble chitosan), a regulator C group (boric acid, citric acid and coconut oil acid diethanolamide) and an auxiliary agent D group (glycerol); weighing the raw materials in the formula according to the specific gravity for later use; adding the chelating agent A group into a reaction kettle, adding 60% of water at 3000rpm/min, stirring at 75 ℃ for 30min, adding the 50% of auxiliary agent D group, simultaneously adding the organic solvent B group into a stainless steel barrel, adding 10% of water at 8000rpm/min, stirring at 90 ℃ for 30min, adding the 50% of auxiliary agent D group, adding the regulator C group into a glass cup, adding the rest of water at 6000rpm/min, stirring at 75 ℃ for 15min, adding the organic solvent B group into the reaction kettle, stirring at 4000rpm/min, stirring at 75 ℃ for 5min, adding the regulator C group at 4500rpm/min, and stirring at 75 ℃ for 5min until the solution is transparent.
Example 3
Preparation examples
The formula is as follows: every 100 parts by weight of the decontamination solution contains 6 parts of hydroxyethylidene diphosphonic acid, 12 parts of pentasodium diethyltriaminepentaacetate, 8 parts of sodium hexametaphosphate, 6 parts of sodium pyrophosphate, 5 parts of acetylacetone, 6 parts of disodium ethylene diamine tetraacetate, 6 parts of boric acid, 4 parts of glycine, 3 parts of citric acid, 1 part of water-soluble chitosan, 6 parts of glycerol, 10 parts of coconut diethanolamide and the balance of water.
Preparation: according to the attributes of raw materials in the formula, the raw materials are divided into a chelating agent A group (hydroxyl ethylidene diphosphonic acid, diethyl triaminepentaacetic acid pentasodium, sodium hexametaphosphate, sodium pyrophosphate and ethylene diamine tetraacetic acid disodium), an organic solvent B group (acetylacetone, glycine and water-soluble chitosan), a regulator C group (boric acid, citric acid and coconut oil acid diethanolamide) and an auxiliary agent D group (glycerol); weighing the raw materials in the formula according to the specific gravity for later use; adding the chelating agent A group into a reaction kettle, adding 50% of water, 9000rpm/min, stirring at 45 ℃ for 90min, adding the 50% of auxiliary agent D group, simultaneously adding the organic solvent B group into a stainless steel barrel, adding 10% of water, 12000rpm/min, stirring at 70 ℃ for 90min, adding the 50% of auxiliary agent D group, adding the regulator C group into a glass cup, adding the rest of water, 10000rpm/min, stirring at 45 ℃ for 45min, adding the organic solvent B group into the reaction kettle, stirring at 8000rpm/min, stirring at 45 ℃ for 15min, adding the regulator C group at 7500rpm/min, stirring at 45 ℃ for 15min, and stirring until the solution is transparent.
Effect detection evaluation method and experimental data
Producing a batch of decontamination solutions of implementation 1, implementation 2 and implementation 3 according to the production process, respectively carrying out decontamination effect detection evaluation on the decontamination solutions, wherein all detection is adopted for implementation one, and partial detection is adopted for implementation two and implementation three;
the experimental method comprises the following steps:
designing a decontamination experiment of radioactive substances on the skin surface according to GBZ/T216-2009 specification for treating radioactive nuclide pollution on the body surface of a human body, and designing a decontamination experiment of the radioactive substances in the environment according to GB 17567-2009 specification for cleaning and controlling the recycling and reusing of steel, aluminum, nickel and copper of nuclear facilities, GB 18871-2002 basic standards for ionizing radiation protection and radiation source safety and GJB 6976-2010 specification for 2008-missile propellant and first-aid kit group;
common radionuclides: actinides, and: 239 Pu、 241 Am、 235 U、 232 Th、 252 Cf
lanthanide series: 140 La、 144 Ce、 147 Pm
transition metal: 90 Y、 50 Co、 59 Fe
non-metal: 222 Rn、 131 I、 32 P、 18 O
metal: 218 Po、 227 Fr、 137 Ba
considering the half-life period and the ionization intensity of the elements, selecting a representative isotope for experiment from the experimental safety, adopting uranium nitrate for actinide, cerium nitrate for lanthanide, cobalt nitrate for transition metal, sodium iodide [131I ] for nonmetal, barium nitrate for metal, and configuring 1000ng/mL of the compound by using a 3% dilute nitric acid solution as a pollution solution to verify the decontamination solution for actinide, lanthanide, transition metal, nonmetal and metal radionuclide decontamination effect; the pollution objects are stainless steel, rubber, cement floors, cotton cloth and white rats and are used for verifying the decontamination effect of the decontamination solution on different environments, the pollution time is 10min, 60min and 120min, the decontamination effect of the decontamination solution on different pollution times is verified, the experimental group is the decontamination solution, the blank group is the background, the contrast group is distilled water contrast decontamination, and the decontamination receptor is decontaminated by the same method and is sampled and detected to verify the decontamination effect of the decontamination solution on the distilled water;
the detection method comprises the following steps:
before the test, the normal work of the tested decontamination equipment is firstly checked, and whether the experimental receptor material is cleaned or not is judged. And carrying out a decontamination efficiency detection test after the conditions are met.
Preparing 1000ng/mL uranium nitrate, cerium nitrate, cobalt nitrate and barium nitrate solutions by using a 3% dilute nitric acid solution respectively, and preparing a 108Bq/L active sodium iodide [131I ] solution as a polluted solution for later use by using distilled water;
for the operations of uranium nitrate, cerium nitrate, cobalt nitrate and barium nitrate, experimental receptors are respectively placed in trays, 2mL of pollution liquid is uniformly smeared on each experimental receptor, after the pollution time is met, 50mL of the pollution liquid is extracted by an injector to wash the experimental receptors twice, and the surfaces of the experimental receptors are continuously washed by a toothbrush for 3 minutes in the washing process. Extracting 2.5ml of decontaminated mixed liquid in a tray by using a liquid-transferring gun to a 50ml colorimetric tube, diluting to 50ml of constant volume, marking a serial number, detecting the concentration of each element in the front polluted liquid and the rear decontamination liquid by adopting ICP-MS (inductively coupled plasma-mass spectrometry), and calculating the mass loss before and after calculation on the premise of fixing the volume of each liquid, namely the decontamination efficiency of the corresponding element under decontamination of the decontamination liquid.
2mL of pollution liquid is uniformly coated on each test receptor for the radioactive iodine [131I ] sodium solution, after the pollution time is met, 50mL of decontamination liquid is extracted by an injector to wash the test receptors for twice, and the surface of the test receptors is continuously washed by a toothbrush for 3 minutes in the washing process. Measuring the radioactive intensity before decontamination by adopting a surface contamination detector at the same parallel height (5 mm +/-1 mm), and calculating the radioactive intensity ratio before and after calculation to obtain the decontamination efficiency of the decontamination solution;
and (4) calculating a result:
for uranium nitrate, cerium nitrate, cobalt nitrate and barium nitrate:
Figure BDA0003788440470000081
in equation (1):
DR-is decontamination efficiency,%;
na-is the concentration of each element before decontamination, ng/mL;
nb is the concentration of each element of the mixed solution after decontamination, ng/mL;
SB-concentration of each element for test receptor blank, ng/mL;
for radioiodine [131I ] sodium salt solution:
Figure BDA0003788440470000082
in formula (2):
DR- -is decontamination efficiency,%;
na-is the radioactivity measurement of the pre-decontamination test, cps(s) -1 );
Nb- -is the measured radioactivity, cps (S), of the post decontamination test -1 );
Pb-is the background count of the test surface, cps(s) -1 )。
The results are shown in tables 1-4:
table 1 example 1 decontamination liquid effectiveness test:
Figure BDA0003788440470000091
Figure BDA0003788440470000101
table 2: further example 1 test of the effectiveness of the decontaminating liquid as shown in the following table:
Figure BDA0003788440470000111
remarking: the experimental procedure adopted 10 8 Bq/L Activity iodine [131I]Sodium dissolving solution, waste water and waste in the experimental process
Sealing and isolating;
table 3: example 2 the efficacy test of the decontaminating liquid is as follows:
Figure BDA0003788440470000121
table 4 example 3 test of the effectiveness of the decontaminating liquid as shown in the following table
Figure BDA0003788440470000131
Data analysis and assay evaluation of tables 1-4
1: the decontamination solutions of the embodiment 1, the embodiment 2 and the embodiment 3 have high decontamination efficiency for actinide radionuclide, lanthanide radionuclide, transition metal radionuclide, nonmetal radionuclide and metal radionuclide, and have decontamination efficiency of more than 90% for different environments such as stainless steel, rubber, cement floor, cotton cloth and skin surface under the action of different contamination time; the decontamination efficiency is 95% in 10 minutes of contamination, and 90% in 120 minutes of contamination; the control group adopts distilled water to carry out the same operation, the decontamination efficiency is about 25 percent in average under the action of 10 minutes of contamination, and the decontamination efficiency is about 20 percent in average 120 minutes of contamination; the transverse direction and the longitudinal direction show that the decontamination solution of the invention is superior to the products of the same series;
2: the decontamination strength of the decontamination solution can be proved by adopting an isotope detection method and a radioactive intensity detection method, namely the decontamination solution still has good decontamination effect on radioactive nuclides;
3: the decontamination solution can effectively face various use environments, a common scrubbing tool is adopted to carry out conventional operation, so that high decontamination efficiency can be achieved, a special scrubbing instrument is not needed, the decontamination process is convenient to carry and develop, the response speed is higher, the use method is simpler, effective decontamination can be achieved only by scrubbing for 3 minutes, radioactive injury is reduced while the time is saved, the radioactive diffusion trend is effectively controlled, and the radioactive accident level is reduced.
The above examples are only illustrative of a limited number of preferred embodiments of the present invention, and are described in more detail and detail, but are not to be construed as limiting the scope of the invention. It should be noted that, for a person skilled in the art, several variations and modifications can be made without departing from the inventive concept, which falls within the scope of the present invention.

Claims (10)

1. A radioactive contamination decontamination solution is characterized in that,
consists of a chelating agent A group, an organic solvent B group, a regulator C group and an auxiliary agent D group;
based on 100 parts by weight:
the group A chelating agents include: 3-6 parts of hydroxyethylidene diphosphonic acid, 8-12 parts of pentasodium diethyltriaminepentaacetate, 2-8 parts of sodium hexametaphosphate, 3-6 parts of sodium pyrophosphate and 3-6 parts of disodium ethylene diamine tetraacetate;
the organic solvent B group comprises: 3-5 parts of acetylacetone, 2-4 parts of glycine and 0.1-1 part of water-soluble chitosan;
the group C modulators include: 3-6 parts of boric acid, 1-3 parts of citric acid and 4-10 parts of coconut diethanolamide; the auxiliary agent group D comprises: 3-6 parts of glycerol;
the balance being water.
2. A radioactive contamination decontamination solution, according to claim 1, wherein said hydroxyethylidene diphosphonic acid is replaced by one of aminotrimethylenephosphonic acid, ethylenediaminetetramethylenephosphonic acid, tetrasodium hydroxyethylidene diphosphonic acid, polyaminopolyether methylenephosphonic acid, diethylenetriaminepentamethylenephosphonic acid, 2-phosphonobutane-1,2,4-tricarboxylic acid.
3. The radioactive contamination decontamination solution of claim 1, wherein the pentasodium diethyltriamine pentaacetate is replaced with one of itaconic acid, calcium disodium diethylenetriamine pentaacetate, and polyethyleneimine.
4. A radioactive contamination decontamination solution according to claim 1, wherein the sodium hexametaphosphate is replaced by one of sodium pyrophosphate, sodium tripolyphosphate and sodium dihydrogen phosphate.
5. A radioactive contamination decontamination solution according to claim 1, wherein the disodium edetate is replaced by one of sodium gluconate and ethylenediaminetetraacetic acid.
6. The radioactive contamination decontamination solution of claim 1, wherein the acetylacetone is replaced with one of sodium polyacrylate, polyepoxysuccinic acid (sodium), and benzotriazole (sodium).
7. A radioactive contamination decontamination solution according to claim 1, wherein the glycine is replaced by one of polyaspartic acid (sodium) and sodium hyaluronate.
8. A radioactive contamination decontamination solution according to claim 1, wherein the water soluble chitosan is replaced by one of polylactic acid, polyglycolic acid, water soluble silica gel; the boric acid is replaced by one of sodium borate and borax; the citric acid is replaced by one of tartaric acid, sodium citrate and metaphosphoric acid; the coconut diethanolamide is replaced by one of sodium dodecyl polyoxyethylene ether sulfate, fatty alcohol polyoxyethylene ether, disodium sulfosuccinate monoester, cocamidopropyl betaine and sodium dodecyl benzene sulfonate; the glycerol is replaced by one of polyethylene glycol and butanediol.
9. The method of preparing a radioactive contamination decontamination solution of any one of claims 1-8, comprising the steps of:
weighing the raw materials in the formula according to the specific weight for later use, adding all the chelating agents A into a reaction kettle, adding 50% of water at 3000-9000rpm/min, stirring at 45-75 ℃ for 30-90min, adding 50% of the auxiliaries D, adding all the organic solvents B into a stainless steel barrel, adding 10% of water at 8000-12000rpm/min, stirring at 70-90 ℃ for 30-90min, adding all the regulators C into a glass cup, adding 40% of water at 6000-10000rpm/min, stirring at 45-75 ℃ for 15-45min, adding the organic solvents B into the reaction kettle, stirring at 4000-8000rpm/min at 45-75 ℃ for 5-15min, adding the regulators C at 4500-7500rpm/min, stirring at 45-75 ℃ for 5-15min, and stirring at 45-75 ℃ for 5-15min until the solution is transparent.
10. Use of a radioactive contamination decontamination solution according to any one of the claims 1-8 for the removal of contamination by actinides, lanthanides, transition metal, non-metal, metal radionuclides.
CN202210948569.5A 2022-08-09 2022-08-09 Radioactive contamination decontamination solution and preparation and application thereof Pending CN115322840A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202210948569.5A CN115322840A (en) 2022-08-09 2022-08-09 Radioactive contamination decontamination solution and preparation and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202210948569.5A CN115322840A (en) 2022-08-09 2022-08-09 Radioactive contamination decontamination solution and preparation and application thereof

Publications (1)

Publication Number Publication Date
CN115322840A true CN115322840A (en) 2022-11-11

Family

ID=83921384

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202210948569.5A Pending CN115322840A (en) 2022-08-09 2022-08-09 Radioactive contamination decontamination solution and preparation and application thereof

Country Status (1)

Country Link
CN (1) CN115322840A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115869212A (en) * 2022-12-09 2023-03-31 中国辐射防护研究院 Transition metal nuclide body surface pollution decontamination agent and preparation method thereof
CN115960685A (en) * 2022-12-09 2023-04-14 中国辐射防护研究院 Actinide nuclide body surface pollution decontamination liquid and preparation method thereof

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009052955A (en) * 2007-08-24 2009-03-12 Toden Kogyo Co Ltd Decontamination liquid, decontamination method, and decontamination system of radioactive contaminant
CN102358875A (en) * 2011-09-29 2012-02-22 广东环凯微生物科技有限公司 Novel acidic detergent for container of food industry
KR20120126849A (en) * 2011-05-13 2012-11-21 주식회사 엔바이로코리아 the composite of removing the radioactive hazardous matearials and the removing method thereof
CN104178027A (en) * 2014-08-22 2014-12-03 西南科技大学 Preparation and application methods of biomass-based self-disintegrating radioactive contamination detergent
CN109288698A (en) * 2018-11-19 2019-02-01 巩义市宏盛稀有金属有限公司 A kind of compound hand cleanser and preparation method thereof for industrial duplicate removal greasy dirt
CN111870595A (en) * 2020-07-31 2020-11-03 湖南福嘉环境安全科技有限公司 Nuclide decontamination solution and preparation method and application thereof
CN111979061A (en) * 2019-05-23 2020-11-24 合肥科源应用化工研究所 Foam detergent for nuclear facilities and preparation method thereof
CN114231361A (en) * 2021-11-23 2022-03-25 中国辐射防护研究院 Radionuclide decontamination composition, product and use thereof

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009052955A (en) * 2007-08-24 2009-03-12 Toden Kogyo Co Ltd Decontamination liquid, decontamination method, and decontamination system of radioactive contaminant
KR20120126849A (en) * 2011-05-13 2012-11-21 주식회사 엔바이로코리아 the composite of removing the radioactive hazardous matearials and the removing method thereof
CN102358875A (en) * 2011-09-29 2012-02-22 广东环凯微生物科技有限公司 Novel acidic detergent for container of food industry
CN104178027A (en) * 2014-08-22 2014-12-03 西南科技大学 Preparation and application methods of biomass-based self-disintegrating radioactive contamination detergent
CN109288698A (en) * 2018-11-19 2019-02-01 巩义市宏盛稀有金属有限公司 A kind of compound hand cleanser and preparation method thereof for industrial duplicate removal greasy dirt
CN111979061A (en) * 2019-05-23 2020-11-24 合肥科源应用化工研究所 Foam detergent for nuclear facilities and preparation method thereof
CN111870595A (en) * 2020-07-31 2020-11-03 湖南福嘉环境安全科技有限公司 Nuclide decontamination solution and preparation method and application thereof
CN114231361A (en) * 2021-11-23 2022-03-25 中国辐射防护研究院 Radionuclide decontamination composition, product and use thereof

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115869212A (en) * 2022-12-09 2023-03-31 中国辐射防护研究院 Transition metal nuclide body surface pollution decontamination agent and preparation method thereof
CN115960685A (en) * 2022-12-09 2023-04-14 中国辐射防护研究院 Actinide nuclide body surface pollution decontamination liquid and preparation method thereof

Similar Documents

Publication Publication Date Title
CN115322840A (en) Radioactive contamination decontamination solution and preparation and application thereof
TWI595506B (en) Process to decontaminate radioactively contaminated surfaces of the components of the cooling system of a nuclear power plant
CN111870595B (en) Nuclide decontamination solution and preparation method and application thereof
US3615817A (en) Method of decontaminating radioactive metal surfaces
JP4443049B2 (en) Degreasing composition and method of using the composition
US8702868B2 (en) Method for decontaminating surfaces of nuclear plants which have been contaminated with alpha emitters
US3033795A (en) Compositions and process for removal of radioactive contaminants
KR100679562B1 (en) A removal of radioactive contaminant
KR810000984B1 (en) Cleaning agent for radioactive stains
CN114085676B (en) Radioactive contaminated soil cleaning agent composition, cleaning agent, preparation method and application thereof
US3113007A (en) Scavenging of radioactive aerosols
CN115869213A (en) Radioactive contaminated skin decontamination agent and preparation method thereof
RU2066495C1 (en) Method of atomic power stations equipment in rooms surface decontamination
KR20240058373A (en) Decontamination compositon
CN115887263A (en) Decontamination agent for nuclide pollution of wound and preparation method thereof
RU2124768C1 (en) Method for decontaminating solid phase of heterogeneous radioactive wastes
CN115463047A (en) Human body surface decontaminating agent for removing transition metal nuclide pollution and preparation method thereof
Menetrez et al. Natural Radioactivity in North Carolina Ground Water Supplies
Setter et al. Measurement of low-level radioactivity in water
Kudryavtsev DEVELOPMENT OF TECHNOLOGY TO PRODUCE DECONTAMINANTS AND DETERGENTS FOR THE NUCLEAR INDUSTRY.
Januska et al. Decontamination of plutonium-contaminated gloveboxes
Nwodo Victor et al. Annual effective dose estimation due to gross alpha and beta activities in groundwater samples from breweries in Nigeria
Hoffman et al. Determining the collection efficiency of gummed paper for the deposition of radioactive contaminants in simulated rain
Abdel Geleel et al. Decontamination of 125 I in Medical Laboratory
RU2586967C1 (en) Method of decontaminating radioactive-contaminated metal and non-metal surfaces

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