CN115477474A - Iron phosphate glass bead for radioactive nuclear waste solidification treatment and preparation method thereof - Google Patents
Iron phosphate glass bead for radioactive nuclear waste solidification treatment and preparation method thereof Download PDFInfo
- Publication number
- CN115477474A CN115477474A CN202211072009.4A CN202211072009A CN115477474A CN 115477474 A CN115477474 A CN 115477474A CN 202211072009 A CN202211072009 A CN 202211072009A CN 115477474 A CN115477474 A CN 115477474A
- Authority
- CN
- China
- Prior art keywords
- glass
- glass beads
- iron phosphate
- phosphate glass
- furnace
- 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
Links
- 239000011324 bead Substances 0.000 title claims abstract description 82
- 239000005365 phosphate glass Substances 0.000 title claims abstract description 36
- 229910000398 iron phosphate Inorganic materials 0.000 title claims abstract description 31
- WBJZTOZJJYAKHQ-UHFFFAOYSA-K iron(3+) phosphate Chemical compound [Fe+3].[O-]P([O-])([O-])=O WBJZTOZJJYAKHQ-UHFFFAOYSA-K 0.000 title claims abstract description 30
- 239000002699 waste material Substances 0.000 title claims abstract description 26
- 238000002360 preparation method Methods 0.000 title claims abstract description 10
- 230000002285 radioactive effect Effects 0.000 title claims abstract description 9
- 238000007711 solidification Methods 0.000 title claims description 11
- 230000008023 solidification Effects 0.000 title claims description 11
- 239000011521 glass Substances 0.000 claims abstract description 135
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims abstract description 62
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 33
- 239000000498 cooling water Substances 0.000 claims abstract description 9
- 229910001220 stainless steel Inorganic materials 0.000 claims abstract description 9
- 239000010935 stainless steel Substances 0.000 claims abstract description 9
- 229910052788 barium Inorganic materials 0.000 claims abstract description 5
- 229910052744 lithium Inorganic materials 0.000 claims abstract description 5
- 229910052749 magnesium Inorganic materials 0.000 claims abstract description 5
- 229910052700 potassium Inorganic materials 0.000 claims abstract description 5
- 239000002994 raw material Substances 0.000 claims abstract description 5
- 238000004140 cleaning Methods 0.000 claims abstract 3
- 238000007873 sieving Methods 0.000 claims abstract 3
- 238000003825 pressing Methods 0.000 claims abstract 2
- 239000000203 mixture Substances 0.000 claims description 32
- 239000000156 glass melt Substances 0.000 claims description 17
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 17
- 238000000137 annealing Methods 0.000 claims description 11
- 238000000034 method Methods 0.000 claims description 11
- 239000008367 deionised water Substances 0.000 claims description 9
- 229910021641 deionized water Inorganic materials 0.000 claims description 9
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims description 8
- QXJJQWWVWRCVQT-UHFFFAOYSA-K calcium;sodium;phosphate Chemical compound [Na+].[Ca+2].[O-]P([O-])([O-])=O QXJJQWWVWRCVQT-UHFFFAOYSA-K 0.000 claims description 8
- 238000001035 drying Methods 0.000 claims description 8
- 238000003756 stirring Methods 0.000 claims description 8
- 238000004017 vitrification Methods 0.000 claims description 8
- 229910052712 strontium Inorganic materials 0.000 claims description 6
- 229910052783 alkali metal Inorganic materials 0.000 claims description 4
- 150000001340 alkali metals Chemical class 0.000 claims description 4
- 229910052784 alkaline earth metal Inorganic materials 0.000 claims description 4
- 150000001342 alkaline earth metals Chemical class 0.000 claims description 4
- 229910052791 calcium Inorganic materials 0.000 claims description 4
- 229910052708 sodium Inorganic materials 0.000 claims description 4
- 238000010298 pulverizing process Methods 0.000 claims description 3
- 238000002844 melting Methods 0.000 abstract description 23
- 230000008018 melting Effects 0.000 abstract description 23
- 239000007788 liquid Substances 0.000 abstract description 8
- 238000005303 weighing Methods 0.000 abstract description 6
- 238000001816 cooling Methods 0.000 abstract description 3
- 229910018072 Al 2 O 3 Inorganic materials 0.000 abstract description 2
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Substances [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 abstract description 2
- 238000002156 mixing Methods 0.000 abstract 2
- 229910015902 Bi 2 O 3 Inorganic materials 0.000 abstract 1
- 229910004298 SiO 2 Inorganic materials 0.000 abstract 1
- 238000003723 Smelting Methods 0.000 abstract 1
- 239000011259 mixed solution Substances 0.000 abstract 1
- 238000012216 screening Methods 0.000 abstract 1
- 238000005245 sintering Methods 0.000 abstract 1
- 239000011734 sodium Substances 0.000 description 9
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 8
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 8
- 229910052760 oxygen Inorganic materials 0.000 description 8
- 239000001301 oxygen Substances 0.000 description 8
- 239000000126 substance Substances 0.000 description 8
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 7
- 230000009471 action Effects 0.000 description 7
- 239000005388 borosilicate glass Substances 0.000 description 6
- WGLPBDUCMAPZCE-UHFFFAOYSA-N chromium trioxide Inorganic materials O=[Cr](=O)=O WGLPBDUCMAPZCE-UHFFFAOYSA-N 0.000 description 6
- 239000002927 high level radioactive waste Substances 0.000 description 6
- 239000000463 material Substances 0.000 description 6
- 239000011159 matrix material Substances 0.000 description 6
- ZOKXTWBITQBERF-UHFFFAOYSA-N Molybdenum Chemical compound [Mo] ZOKXTWBITQBERF-UHFFFAOYSA-N 0.000 description 5
- 238000002441 X-ray diffraction Methods 0.000 description 5
- 229910000416 bismuth oxide Inorganic materials 0.000 description 5
- 229910000423 chromium oxide Inorganic materials 0.000 description 5
- TYIXMATWDRGMPF-UHFFFAOYSA-N dibismuth;oxygen(2-) Chemical compound [O-2].[O-2].[O-2].[Bi+3].[Bi+3] TYIXMATWDRGMPF-UHFFFAOYSA-N 0.000 description 5
- 239000007789 gas Substances 0.000 description 5
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N iron oxide Inorganic materials [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 5
- 229910052750 molybdenum Inorganic materials 0.000 description 5
- 239000011733 molybdenum Substances 0.000 description 5
- TWNQGVIAIRXVLR-UHFFFAOYSA-N oxo(oxoalumanyloxy)alumane Chemical compound O=[Al]O[Al]=O TWNQGVIAIRXVLR-UHFFFAOYSA-N 0.000 description 5
- NDLPOXTZKUMGOV-UHFFFAOYSA-N oxo(oxoferriooxy)iron hydrate Chemical compound O.O=[Fe]O[Fe]=O NDLPOXTZKUMGOV-UHFFFAOYSA-N 0.000 description 5
- 230000008569 process Effects 0.000 description 5
- 229910052814 silicon oxide Inorganic materials 0.000 description 5
- 239000013078 crystal Substances 0.000 description 4
- 229910052761 rare earth metal Inorganic materials 0.000 description 4
- 229910000029 sodium carbonate Inorganic materials 0.000 description 4
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 3
- QCWXUUIWCKQGHC-UHFFFAOYSA-N Zirconium Chemical compound [Zr] QCWXUUIWCKQGHC-UHFFFAOYSA-N 0.000 description 3
- LFVGISIMTYGQHF-UHFFFAOYSA-N ammonium dihydrogen phosphate Chemical compound [NH4+].OP(O)([O-])=O LFVGISIMTYGQHF-UHFFFAOYSA-N 0.000 description 3
- 229910000387 ammonium dihydrogen phosphate Inorganic materials 0.000 description 3
- 238000002425 crystallisation Methods 0.000 description 3
- 238000007496 glass forming Methods 0.000 description 3
- 238000002386 leaching Methods 0.000 description 3
- 235000019837 monoammonium phosphate Nutrition 0.000 description 3
- 150000002910 rare earth metals Chemical class 0.000 description 3
- 239000000758 substrate Substances 0.000 description 3
- 229910052717 sulfur Inorganic materials 0.000 description 3
- 239000011593 sulfur Substances 0.000 description 3
- 238000012360 testing method Methods 0.000 description 3
- 229910052726 zirconium Inorganic materials 0.000 description 3
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 2
- 229910021193 La 2 O 3 Inorganic materials 0.000 description 2
- 229910052768 actinide Inorganic materials 0.000 description 2
- 150000001255 actinides Chemical class 0.000 description 2
- AYJRCSIUFZENHW-DEQYMQKBSA-L barium(2+);oxomethanediolate Chemical compound [Ba+2].[O-][14C]([O-])=O AYJRCSIUFZENHW-DEQYMQKBSA-L 0.000 description 2
- 230000008901 benefit Effects 0.000 description 2
- 229910052792 caesium Inorganic materials 0.000 description 2
- TVFDJXOCXUVLDH-UHFFFAOYSA-N caesium atom Chemical compound [Cs] TVFDJXOCXUVLDH-UHFFFAOYSA-N 0.000 description 2
- 239000011575 calcium Substances 0.000 description 2
- 239000000919 ceramic Substances 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 230000008025 crystallization Effects 0.000 description 2
- YWEUIGNSBFLMFL-UHFFFAOYSA-N diphosphonate Chemical compound O=P(=O)OP(=O)=O YWEUIGNSBFLMFL-UHFFFAOYSA-N 0.000 description 2
- 238000010438 heat treatment Methods 0.000 description 2
- 239000012535 impurity Substances 0.000 description 2
- 239000011777 magnesium Substances 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- DTEMQJHXKZCSMQ-UHFFFAOYSA-J phosphonato phosphate;zirconium(4+) Chemical compound [Zr+4].[O-]P([O-])(=O)OP([O-])([O-])=O DTEMQJHXKZCSMQ-UHFFFAOYSA-J 0.000 description 2
- DLYUQMMRRRQYAE-UHFFFAOYSA-N phosphorus pentoxide Inorganic materials O1P(O2)(=O)OP3(=O)OP1(=O)OP2(=O)O3 DLYUQMMRRRQYAE-UHFFFAOYSA-N 0.000 description 2
- BWHMMNNQKKPAPP-UHFFFAOYSA-L potassium carbonate Chemical compound [K+].[K+].[O-]C([O-])=O BWHMMNNQKKPAPP-UHFFFAOYSA-L 0.000 description 2
- 239000000843 powder Substances 0.000 description 2
- 230000005855 radiation Effects 0.000 description 2
- 239000002901 radioactive waste Substances 0.000 description 2
- 238000005096 rolling process Methods 0.000 description 2
- CIOAGBVUUVVLOB-UHFFFAOYSA-N strontium atom Chemical compound [Sr] CIOAGBVUUVVLOB-UHFFFAOYSA-N 0.000 description 2
- 229910019142 PO4 Inorganic materials 0.000 description 1
- 239000004809 Teflon Substances 0.000 description 1
- 229920006362 Teflon® Polymers 0.000 description 1
- AFCIMSXHQSIHQW-UHFFFAOYSA-N [O].[P] Chemical compound [O].[P] AFCIMSXHQSIHQW-UHFFFAOYSA-N 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- WMWLMWRWZQELOS-UHFFFAOYSA-N bismuth(III) oxide Inorganic materials O=[Bi]O[Bi]=O WMWLMWRWZQELOS-UHFFFAOYSA-N 0.000 description 1
- 229910000019 calcium carbonate Inorganic materials 0.000 description 1
- 229940117975 chromium trioxide Drugs 0.000 description 1
- GAMDZJFZMJECOS-UHFFFAOYSA-N chromium(6+);oxygen(2-) Chemical compound [O-2].[O-2].[O-2].[Cr+6] GAMDZJFZMJECOS-UHFFFAOYSA-N 0.000 description 1
- 238000004031 devitrification Methods 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 238000011038 discontinuous diafiltration by volume reduction Methods 0.000 description 1
- 230000005674 electromagnetic induction Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000011156 evaluation Methods 0.000 description 1
- 238000009472 formulation Methods 0.000 description 1
- 239000002241 glass-ceramic Substances 0.000 description 1
- 231100001261 hazardous Toxicity 0.000 description 1
- 239000002920 hazardous waste Substances 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- BDAGIHXWWSANSR-NJFSPNSNSA-N hydroxyformaldehyde Chemical compound O[14CH]=O BDAGIHXWWSANSR-NJFSPNSNSA-N 0.000 description 1
- 230000006698 induction Effects 0.000 description 1
- 238000002354 inductively-coupled plasma atomic emission spectroscopy Methods 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- XGZVUEUWXADBQD-UHFFFAOYSA-L lithium carbonate Chemical compound [Li+].[Li+].[O-]C([O-])=O XGZVUEUWXADBQD-UHFFFAOYSA-L 0.000 description 1
- 229910052808 lithium carbonate Inorganic materials 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 239000000395 magnesium oxide Substances 0.000 description 1
- CPLXHLVBOLITMK-UHFFFAOYSA-N magnesium oxide Inorganic materials [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 description 1
- AXZKOIWUVFPNLO-UHFFFAOYSA-N magnesium;oxygen(2-) Chemical compound [O-2].[Mg+2] AXZKOIWUVFPNLO-UHFFFAOYSA-N 0.000 description 1
- 239000010812 mixed waste Substances 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 description 1
- 239000010452 phosphate Substances 0.000 description 1
- 125000002467 phosphate group Chemical group [H]OP(=O)(O[H])O[*] 0.000 description 1
- 229910000027 potassium carbonate Inorganic materials 0.000 description 1
- 238000004445 quantitative analysis Methods 0.000 description 1
- 238000012958 reprocessing Methods 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 239000000377 silicon dioxide Substances 0.000 description 1
- 235000012239 silicon dioxide Nutrition 0.000 description 1
- 230000003595 spectral effect Effects 0.000 description 1
- 239000002915 spent fuel radioactive waste Substances 0.000 description 1
- 230000006641 stabilisation Effects 0.000 description 1
- 238000011105 stabilization Methods 0.000 description 1
- 238000007655 standard test method Methods 0.000 description 1
- 238000003860 storage Methods 0.000 description 1
- 229910000018 strontium carbonate Inorganic materials 0.000 description 1
- 230000007704 transition Effects 0.000 description 1
Images
Classifications
-
- C—CHEMISTRY; METALLURGY
- C03—GLASS; MINERAL OR SLAG WOOL
- C03C—CHEMICAL COMPOSITION OF GLASSES, GLAZES OR VITREOUS ENAMELS; SURFACE TREATMENT OF GLASS; SURFACE TREATMENT OF FIBRES OR FILAMENTS MADE FROM GLASS, MINERALS OR SLAGS; JOINING GLASS TO GLASS OR OTHER MATERIALS
- C03C12/00—Powdered glass; Bead compositions
-
- C—CHEMISTRY; METALLURGY
- C03—GLASS; MINERAL OR SLAG WOOL
- C03B—MANUFACTURE, SHAPING, OR SUPPLEMENTARY PROCESSES
- C03B19/00—Other methods of shaping glass
- C03B19/10—Forming beads
- C03B19/1005—Forming solid beads
-
- C—CHEMISTRY; METALLURGY
- C03—GLASS; MINERAL OR SLAG WOOL
- C03B—MANUFACTURE, SHAPING, OR SUPPLEMENTARY PROCESSES
- C03B19/00—Other methods of shaping glass
- C03B19/10—Forming beads
- C03B19/1095—Thermal after-treatment of beads, e.g. tempering, crystallisation, annealing
-
- G—PHYSICS
- G21—NUCLEAR PHYSICS; NUCLEAR ENGINEERING
- G21F—PROTECTION AGAINST X-RADIATION, GAMMA RADIATION, CORPUSCULAR RADIATION OR PARTICLE BOMBARDMENT; TREATING RADIOACTIVELY CONTAMINATED MATERIAL; DECONTAMINATION ARRANGEMENTS THEREFOR
- G21F9/00—Treating radioactively contaminated material; Decontamination arrangements therefor
- G21F9/04—Treating liquids
- G21F9/06—Processing
- G21F9/16—Processing by fixation in stable solid media
- G21F9/162—Processing by fixation in stable solid media in an inorganic matrix, e.g. clays, zeolites
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Materials Engineering (AREA)
- Manufacturing & Machinery (AREA)
- Physics & Mathematics (AREA)
- High Energy & Nuclear Physics (AREA)
- General Engineering & Computer Science (AREA)
- Inorganic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Geochemistry & Mineralogy (AREA)
- Thermal Sciences (AREA)
- Glass Compositions (AREA)
Abstract
Description
技术领域technical field
本发明涉及一种铁磷酸盐玻璃珠、制备方法及其应用,用于放射性核废料的固化处理,特别适用于核工业等领域所排放的高放射性核废料的固化处理。The invention relates to an iron phosphate glass bead, a preparation method and an application thereof, which are used for solidification treatment of radioactive nuclear waste, and are especially suitable for solidification treatment of high radioactive nuclear waste discharged in fields such as the nuclear industry.
背景技术Background technique
核能作为一种无污染、几乎零排放的清洁能源,得到了广泛的发展,然而核能利用过程中会产生大量的放射性废物,其处理和处置问题也日益显现,成为全世界关注的难题。为了把放射性核素牢固地结合到稳定的惰性基材中,满足安全处置的要求,一般会对废物进行固化处理。玻璃固化作为第一代高放废物固化技术,是目前唯一实现了工业化运行的固化处理方法,也是目前人们普遍接受并且满足安全处置的形式之一。玻璃固化具体是指在高温下熔融废物中的无机成分,在冷却后,形成玻璃或者类似于玻璃的物质,从而使放射性核素固定在玻璃网络中实现稳定化。其优点在于对放射性核素无选择性,几乎可以固化高放废液中的所有组分,而且玻璃固化体的浸出率较低,减容比大,辐照性和导热性能都较好。随着世界上第一个玻璃固化设施在法国马库尔AVM投入运行,英国、美国、比利时、俄罗斯、日本等国家也逐步实现玻璃固化工业化。Nuclear energy, as a clean energy with no pollution and almost zero emissions, has been widely developed. However, the use of nuclear energy will generate a large amount of radioactive waste, and the problem of its treatment and disposal has become increasingly apparent, which has become a problem of worldwide concern. In order to firmly incorporate radionuclides into a stable inert substrate and meet the requirements for safe disposal, the waste is generally immobilized. As the first generation of solidification technology for high-level radioactive waste, vitrification is currently the only solidification treatment method that has realized industrial operation, and it is also one of the forms that are generally accepted by people and satisfy safe disposal. Vitrification specifically refers to the melting of inorganic components in waste at high temperature, and after cooling, glass or glass-like substances are formed, so that radionuclides are fixed in the glass network to achieve stabilization. Its advantage is that it has no selectivity to radionuclides, can solidify almost all components in high-level waste liquid, and has a low leaching rate of the glass solidified body, a large volume reduction ratio, and good radiation and thermal conductivity. With the world's first vitrification facility put into operation in Marcourt AVM, France, countries such as the United Kingdom, the United States, Belgium, Russia, and Japan have also gradually realized the industrialization of vitrification.
核废料玻璃固化工艺过程一般来说是直接在高放射性废液或者在将其煅烧后的煅烧料中,按比例投入用于包容核废物的基质玻璃珠,在焦耳陶瓷加热炉或者高频感应炉中熔制、均化、漏料,然后固化成玻璃,把放射性核废物固定在玻璃中。为了熔制方便,增加固化效率,一般先熔制基质玻璃,并预先处理,制备成便于工艺顺利实现的玻璃珠。选用玻璃珠,因为玻璃珠滚动性好,生产工艺方便,可以容易的与核废物混合加入熔炉中快速熔化。Generally speaking, the nuclear waste vitrification process is directly in the highly radioactive waste liquid or in the calcined material after it is calcined, and puts the matrix glass beads used to contain the nuclear waste in proportion, in a Joule ceramic heating furnace or a high frequency induction furnace It is melted, homogenized, leaked, and then solidified into glass, and the radioactive nuclear waste is fixed in the glass. In order to facilitate melting and increase curing efficiency, the matrix glass is usually melted first and pre-treated to prepare glass beads that facilitate the smooth realization of the process. Glass beads are selected, because the glass beads have good rolling properties and the production process is convenient, and can be easily mixed with nuclear waste and added to the furnace for rapid melting.
用于玻璃固化处理的玻璃珠材料,首先是基质玻璃包容性好,可以包容一定含量的核废物,在熔炉中可以跟核废物快速反应生成均匀的高温玻璃熔体,然后通过出料工艺得到固化性能良好的玻璃固化体;其次是成玻璃性好,这对于玻璃珠的制备非常重要,易析晶的玻璃基质很难快速成球。合格的基质玻璃珠玻璃透明,不容易发生粘结,在固化处理的时候快速滚动进入熔化器,增加核废物固化玻璃连续熔炼的工作效率。The glass bead material used for vitrification treatment, first of all, the matrix glass has good tolerance and can contain a certain amount of nuclear waste. It can quickly react with the nuclear waste in the furnace to form a uniform high-temperature glass melt, and then solidify it through the discharging process. It is a vitrified body with good performance; secondly, it has good vitrification property, which is very important for the preparation of glass beads, and it is difficult to quickly form a ball into a glass matrix that is easy to devitrify. Qualified matrix glass beads are transparent, not easy to bond, and quickly roll into the melter during solidification treatment, increasing the efficiency of continuous melting of nuclear waste solidified glass.
专利ZL201010190038.1公布了一种用于固化高放射性核废料的玻璃珠的生产方法,选用的玻璃基材是硼硅酸盐玻璃。硼硅酸盐玻璃可以包容多种氧化物和废物,其固化体具备较好的化学稳定性和辐照稳定性。但对于含有较高浓度的硫、钼等的高放废液来讲,硼硅酸盐玻璃的固化能力有限,会分离产生第二相(黄相),漂浮在玻璃熔液上方,不能均匀的包容进玻璃基体,不能起到固化的作用。且硼硅酸盐玻璃熔制温度过高,对锶、铯等易挥发放射性同位素的固化率偏低。而磷酸盐玻璃的网络结构为磷氧四面体,可通过桥氧相连来形成不同的磷酸盐结构,对钼、硫等元素具有较高的包容性。20世纪90年代中期,美国的研究者研究出了一种具有良好的化学稳定性和热稳定性的新型磷酸盐玻璃—铁磷酸盐玻璃。研究发现Fe3+能进入磷酸盐玻璃网络结构,形成稳定的Fe-O-P键,取代不稳定的P-O-P共价键,从而改善磷酸盐玻璃的化学稳定性。与硼硅酸盐玻璃相比,磷酸盐玻璃固化体还具有较低的熔制温度,玻璃软化温度和转变温度,而且黏度小,玻璃形成范围大,有成为核废料处理固化基材的潜质。Patent ZL201010190038.1 discloses a production method for glass beads used to solidify high-radioactive nuclear waste, and the selected glass substrate is borosilicate glass. Borosilicate glass can contain a variety of oxides and wastes, and its cured body has good chemical stability and radiation stability. However, for high-level waste liquid containing higher concentrations of sulfur, molybdenum, etc., the solidification ability of borosilicate glass is limited, and it will separate to produce a second phase (yellow phase), which floats above the glass melt and cannot be uniformly Included in the glass matrix, can not play the role of curing. Moreover, the melting temperature of borosilicate glass is too high, and the solidification rate of volatile radioactive isotopes such as strontium and cesium is low. The network structure of phosphate glass is phosphorus-oxygen tetrahedron, which can be connected by bridge oxygen to form different phosphate structures, and has a high tolerance for molybdenum, sulfur and other elements. In the mid-1990s, researchers in the United States developed a new type of phosphate glass with good chemical and thermal stability—iron phosphate glass. The study found that Fe 3+ can enter the network structure of phosphate glass to form a stable Fe-OP bond to replace the unstable POP covalent bond, thereby improving the chemical stability of phosphate glass. Compared with borosilicate glass, phosphate vitrified body also has lower melting temperature, glass softening temperature and transition temperature, and has a small viscosity and a wide range of glass formation, and has the potential to become a solidified substrate for nuclear waste treatment.
发明内容Contents of the invention
本发明首先提供了用于制备玻璃珠的铁磷酸盐玻璃基础配方,其成玻璃性能好,包容废物能力强;其次提供了一种用于核废料固化工艺处理的铁磷酸盐玻璃珠的制备方法。The present invention firstly provides the basic formula of iron phosphate glass used for preparing glass beads, which has good glass-forming performance and strong ability to contain waste; secondly, it provides a preparation method of iron phosphate glass beads used in the solidification process of nuclear waste .
本发明的具体技术方案如下:Concrete technical scheme of the present invention is as follows:
一种铁磷酸盐玻璃珠的制备方法,其特点在于:所述玻璃的组成质量百分比为:A preparation method of iron phosphate glass beads is characterized in that: the composition mass percentage of the glass is:
其中M是碱金属Li、Na、K中的一种或几种,Me是碱土金属Mg、Ca、Sr、Ba中的一种或几种。Wherein M is one or more of alkali metals Li, Na and K, and Me is one or more of alkaline earth metals Mg, Ca, Sr and Ba.
本发明还提供了一种上述铁磷酸盐玻璃珠的制备方法,包括以下步骤:The present invention also provides a kind of preparation method of above-mentioned iron phosphate glass beads, comprising the following steps:
(1)、按照玻璃组分及质量百分比计算配方,并称取原材料,混合均匀,得到混合料;(1), calculate formula according to glass component and mass percentage, and take raw material, mix uniformly, obtain compound;
(2)、把混合料盛入坩埚,并在1000~1200℃的电熔炉中熔化后,通入氧气2~4小时,气量为100~120升/小时,得到澄清均匀的玻璃熔体;(2) Put the mixed material into the crucible and melt it in an electric melting furnace at 1000-1200°C, then feed oxygen for 2-4 hours, with a gas volume of 100-120 liters/hour, to obtain a clear and uniform glass melt;
(3)、将澄清均匀的玻璃熔体浇注在通入冷却水的中空不锈钢辊筒上,压制成3mm厚的玻璃片,然后机器粉碎,得到外径1-3mm大小的玻璃块体;(3), pour the clarified and uniform glass melt on the hollow stainless steel roller that feeds cooling water, press it into a glass sheet with a thickness of 3 mm, and then crush it by machine to obtain a glass block with an outer diameter of 1-3 mm;
(4)、把玻璃碎块与石墨粉体按照质量比1:1的比例混合,转移到一个摇摆式电熔炉中,温度设为850-950℃,摇摆频率为30转/分钟,摇摆角度120°,根据玻璃量的不同,快速摇摆15~45分钟,使玻璃块迅速表面软化,并且在表面张力的作用下棱角收缩,随着炉子的摇摆滚动形成玻璃球。转移玻璃球及石墨粉的混合物至400~500℃的退火炉中,退火4小时。然后随炉冷却至室温,过筛,筛出石墨粉,得到直径在1-3mm的玻璃珠。(4) Mix glass pieces and graphite powder according to the mass ratio of 1:1, transfer them to a swing electric melting furnace, set the temperature to 850-950°C, swing frequency to 30 rpm, and swing angle to 120° °, depending on the amount of glass, shake quickly for 15 to 45 minutes to soften the surface of the glass block rapidly, and shrink the edges and corners under the action of surface tension, and form glass balls with the swing of the furnace. Transfer the mixture of glass balls and graphite powder to an annealing furnace at 400-500°C, and anneal for 4 hours. Then cool down to room temperature with the furnace, sieve, and sieve out the graphite powder to obtain glass beads with a diameter of 1-3mm.
(5)、把过筛的玻璃珠投入浓度均为0.3mol/L的Na2CO3/NaOH溶液中,搅拌10~15分钟,使碱液与玻璃珠表面反应,以快速去除玻璃珠表面的石墨粉,再用清水、无水乙醇、去离子水依次冲洗玻璃珠表面的碱液,最后转移到90℃烘箱中烘干,得到铁磷酸盐玻璃珠。(5) Put the sieved glass beads into the Na 2 CO 3 /NaOH solution with a concentration of 0.3 mol/L, and stir for 10 to 15 minutes to make the lye react with the surface of the glass beads to quickly remove the impurities on the surface of the glass beads. Graphite powder, then wash the lye on the surface of the glass beads with clear water, absolute ethanol, and deionized water in sequence, and finally transfer to a 90°C oven for drying to obtain iron phosphate glass beads.
本发明的有益效果在于:乏燃料后处理废物的成份非常复杂,同时包含了较多的容易产生晶相的锆、钼、稀土、锕系元素等。相对于硼硅酸盐玻璃,选择磷酸盐玻璃的优势在于氧磷四面体空间大,结构更为开放,可以容纳更多的稀土、锕系及重金属离子。玻璃成分中添加少量二氧化硅、三氧化二铋和三氧化二铬,少量添加有调节粘度和改善玻璃网络体的作用,含量均控制在2%以下;超过2%,容易产生分相导致玻璃析晶。本发明制备的铁磷酸盐玻璃珠抗析晶能力好,包容废物能力强,且由于玻璃的成玻璃性质较好,成珠工艺的边角料可以回炉重熔,并进行再加工循环利用。The beneficial effect of the present invention is that: the composition of spent fuel reprocessing waste is very complex, and at the same time contains more zirconium, molybdenum, rare earth, actinides and the like which are easy to produce crystal phases. Compared with borosilicate glass, the advantage of choosing phosphate glass is that the oxyphosphorus tetrahedron has a large space and a more open structure, which can accommodate more rare earth, actinide and heavy metal ions. Adding a small amount of silicon dioxide, bismuth trioxide and chromium trioxide to the glass composition can adjust the viscosity and improve the glass network. Crystallization. The iron phosphate glass beads prepared by the invention have good anti-crystallization ability and strong ability to contain waste, and because the glass has good glass-forming properties, the leftover material of the beading process can be returned to the furnace for remelting, and can be reprocessed and recycled.
附图说明Description of drawings
图1玻璃珠磨粉后的X射线衍射图;The X-ray diffraction figure after Fig. 1 glass bead pulverization;
图2包容率为22%的固化玻璃;Fig. 2 solidified glass with 22% containment rate;
图3固化玻璃磨粉后的X射线衍射图;The X-ray diffraction pattern after Fig. 3 solidified glass pulverization;
图4固化玻璃7天化学稳定性的元素浸出数据。Figure 4. Elemental leaching data for 7-day chemical stability of cured glass.
具体实施方式detailed description
实施例中提供的铁磷酸盐玻璃珠的组分质量百分比为:The component mass percentage of the iron phosphate glass beads provided in the embodiment is:
其中M是碱金属Li、Na、K中的一种或几种,Me是碱土金属Mg、Ca、Sr、Ba中的一种或几种。Wherein M is one or more of alkali metals Li, Na and K, and Me is one or more of alkaline earth metals Mg, Ca, Sr and Ba.
实施例中玻璃珠的制备方法包括以下步骤:The preparation method of glass beads in the embodiment comprises the following steps:
(1)、按照玻璃组分及质量百分比计算配方,并称取原材料,混合均匀,得到混合料;(1), calculate formula according to glass component and mass percentage, and take raw material, mix uniformly, obtain compound;
(2)、把混合料盛入坩埚,并在1000~1200℃的电熔炉中熔化后,通入氧气2~4小时,气量为100~120升/小时,得到澄清均匀的玻璃熔体;(2) Put the mixed material into the crucible and melt it in an electric melting furnace at 1000-1200°C, then feed oxygen for 2-4 hours, with a gas volume of 100-120 liters/hour, to obtain a clear and uniform glass melt;
(3)、将澄清均匀的玻璃熔体浇注在通入冷却水的中空不锈钢辊筒上,压制成3mm厚的玻璃片,然后机器粉碎,得到外径1-3mm大小的玻璃块体;(3), pour the clarified and uniform glass melt on the hollow stainless steel roller that feeds cooling water, press it into a glass sheet with a thickness of 3 mm, and then crush it by machine to obtain a glass block with an outer diameter of 1-3 mm;
(4)、把玻璃碎块与石墨粉体按照质量比1:1的比例混合,转移到一个摇摆式电熔炉中,温度设为850-950℃,摇摆频率为30转/分钟,摇摆角度120°,根据玻璃量的不同,快速摇摆15~45分钟,使玻璃块迅速表面软化,并且在表面张力的作用下棱角收缩,随着炉子的摇摆滚动形成玻璃球。转移玻璃球及石墨粉的混合物至400~500℃的退火炉中,退火4小时。然后随炉冷却至室温,过筛,筛出石墨粉,得到直径1-3mm的玻璃珠。(4) Mix glass pieces and graphite powder according to the mass ratio of 1:1, transfer them to a swing electric melting furnace, set the temperature to 850-950°C, swing frequency to 30 rpm, and swing angle to 120° °, depending on the amount of glass, shake quickly for 15 to 45 minutes to soften the surface of the glass block rapidly, and shrink the edges and corners under the action of surface tension, and form glass balls with the swing of the furnace. Transfer the mixture of glass balls and graphite powder to an annealing furnace at 400-500°C, and anneal for 4 hours. Then cool down to room temperature with the furnace, sieve, and sieve out the graphite powder to obtain glass beads with a diameter of 1-3mm.
(5)、把过筛的玻璃珠投入浓度均为0.3mol/L的Na2CO3/NaOH溶液中,搅拌10~15分钟,使碱液与玻璃珠表面反应,以快速去除玻璃珠表面的石墨粉,再用清水、无水乙醇、去离子水依次冲洗玻璃珠表面的碱液,最后转移到90℃烘箱中烘干,得到铁磷酸盐玻璃珠。(5) Put the sieved glass beads into the Na 2 CO 3 /NaOH solution with a concentration of 0.3 mol/L, and stir for 10 to 15 minutes to make the lye react with the surface of the glass beads to quickly remove the impurities on the surface of the glass beads. Graphite powder, then wash the lye on the surface of the glass beads with clear water, absolute ethanol, and deionized water in sequence, and finally transfer to a 90°C oven for drying to obtain iron phosphate glass beads.
表1给出本发明的5个实施例的玻璃配方:Table 1 provides the glass formulations of 5 embodiments of the present invention:
表1Table 1
实施例1:Example 1:
按照表1中实施例1称取磷酸二氢铵85.9克、三氧化二铁8克、氧化铝18克、碳酸钠25.6克、碳酸钡2.9克、氧化铋1.5克、氧化硅1.5克,氧化铬0.5克,混合均匀,得到混合料。在1000℃的电熔炉中熔化后,通入氧气2小时,气量为120升/小时,得到澄清均匀的玻璃熔体。将澄清均匀的玻璃熔体浇注在通入冷却水的中空不锈钢辊筒上,压制成3mm厚的玻璃片,然后机器粉碎,得到外径1-3mm大小的玻璃块体。把玻璃碎块与石墨粉体按照质量比1:1的比例混合,转移到一个摇摆式电熔炉中,温度设为900℃,摇摆频率为30转/分钟,摇摆角度120°,快速摇摆20分钟,使玻璃块迅速表面软化,并且在表面张力的作用下棱角收缩,随着炉子的摇摆滚动形成玻璃球。转移玻璃球及石墨粉的混合物至450℃的退火炉中,退火4小时。然后随炉冷却至室温,过筛,筛出石墨粉,得到直径小于3mm、大于1mm的玻璃珠。把过筛的玻璃珠投入浓度均为0.3mol/L的Na2CO3/NaOH溶液中,搅拌10~15分钟,使碱液与玻璃珠表面反应,以快速去除玻璃珠表面的石墨粉,再用清水、酒精、去离子水依次冲洗玻璃珠表面的碱液,最后转移到90℃烘箱中烘干,得到铁磷酸盐玻璃珠。According to Example 1 in Table 1, take by weighing 85.9 grams of ammonium dihydrogen phosphate, 8 grams of ferric oxide, 18 grams of aluminum oxide, 25.6 grams of sodium carbonate, 2.9 grams of barium carbonate, 1.5 grams of bismuth oxide, 1.5 grams of silicon oxide, chromium oxide 0.5 g, mixed evenly to obtain a mixture. After melting in an electric melting furnace at 1000°C, oxygen was introduced for 2 hours at a gas volume of 120 liters per hour to obtain a clear and uniform glass melt. The clarified and uniform glass melt is poured on a hollow stainless steel roller fed with cooling water, pressed into a 3mm thick glass sheet, and then crushed by a machine to obtain a glass block with an outer diameter of 1-3mm. Mix glass pieces and graphite powder in a mass ratio of 1:1, transfer to a swing-type electric melting furnace, set the temperature to 900°C, swing frequency to 30 rpm, swing angle to 120°, and swing quickly for 20 minutes , so that the surface of the glass block is softened rapidly, and the edges and corners shrink under the action of surface tension, and the glass ball is formed as the furnace swings and rolls. Transfer the mixture of glass spheres and graphite powder to an annealing furnace at 450° C., and anneal for 4 hours. Then cool down to room temperature with the furnace, sieve, and sieve out the graphite powder to obtain glass beads with a diameter less than 3 mm and greater than 1 mm. Put the sieved glass beads into the Na 2 CO 3 /NaOH solution with a concentration of 0.3mol/L, and stir for 10-15 minutes to make the lye react with the surface of the glass beads to quickly remove the graphite powder on the surface of the glass beads, and then Rinse the lye on the surface of the glass beads sequentially with water, alcohol, and deionized water, and finally transfer to an oven at 90°C for drying to obtain iron phosphate glass beads.
把得到的铁磷酸盐玻璃珠磨粉,过200目筛,测试X射线衍射图谱,如图1所示,谱线为典型的无定形峰包,说明玻璃内部无析晶成份,成玻璃性能较好。The obtained iron phosphate glass beads are ground, passed through a 200-mesh sieve, and the X-ray diffraction pattern is tested, as shown in Figure 1, the spectral line is a typical amorphous peak package, indicating that there is no devitrification component in the glass, and the glass-forming performance is relatively good. it is good.
动力堆高放射性废液的常见元素有锆、钼、稀土等成分,模拟高放废液的成份为ZrO2、MoO3、La2O3,用质量比78%的该玻璃珠与质量比22%的模拟高放废液成份(其中包括Cs2O 2%、SrO 3%、ZrO2 4%、MoO3 7%、La2O3 6%)混合均匀,在1200℃高温熔化,得到废物包容率氧化物质量百分比为22%的固化玻璃,如图2所示。The common elements of the high-level radioactive waste liquid of power reactors include zirconium, molybdenum, rare earth and other components. The components of the simulated high-level radioactive waste liquid are ZrO 2 , MoO 3 , and La 2 O 3 . % simulated high-level radioactive waste liquid components (including Cs 2 O 2%, SrO 3%, ZrO 2 4%, MoO 3 7%, La 2 O 3 6%) were mixed evenly, and melted at a high temperature of 1200°C to obtain waste containment The solidified glass with an oxide mass percentage of 22%, as shown in Figure 2.
对固化玻璃磨粉,过200目筛,掺入α-Al2O3粉测试X射线衍射图谱,如图3所示,固化玻璃主体为无定形态,存在少量的晶相,对比标准图谱,解析得到的晶相为叫焦磷酸锆,对X射线衍射图谱进行定量分析,计算的固化玻璃内部的焦磷酸锆晶相占玻璃固化体的体积百分比为1.6%,符合核工业标准EJ1186-2005中,玻璃固化体冷至室温后的析晶率低于5%的标准。For the solidified glass, pass through a 200-mesh sieve and add α-Al 2 O 3 powder to test the X-ray diffraction pattern. As shown in Figure 3, the main body of the solidified glass is in an amorphous state, and there is a small amount of crystal phase. Compared with the standard pattern, The crystal phase obtained by analysis is called zirconium pyrophosphate. Quantitative analysis of the X-ray diffraction pattern shows that the calculated zirconium pyrophosphate crystal phase inside the solidified glass accounts for 1.6% of the volume of the glass solidified body, which is in line with the nuclear industry standard EJ1186-2005. , the crystallization rate of the glass solidified body after cooling to room temperature is lower than the standard of 5%.
使用PCT法评估固化玻璃的化学稳定性,参照美国材料与试验协会发布的标准ASTM C1285-14《Standard test method for determining chemical durability ofnuclear,hazardous,and mixed waste glasses and multiphase glass ceramics:theproduct consistency test(PCT)》中规定的方法。将样品粉碎并过筛,分离出粒度分数为100至200目的粉末,将粉末清洗并干燥至恒重。将每个样品取1.5g放入装有去离子水的聚四氟乙烯容器中。密封后,置90℃的烘箱中7天。使用ICP-OES测量浸出液中各种元素的浓度,通过计算各元素的归一化质量损失来评估化学稳定性,如图4所示,各个元素的归一化浸出率均远远低于1克/(米2·天),符合核废物固化体性能评估的要求,适合地下长期地质存储。Use the PCT method to evaluate the chemical stability of cured glass, referring to the standard ASTM C1285-14 issued by the American Society for Testing and Materials "Standard test method for determining chemical durability of nuclear, hazardous, and mixed waste glasses and multiphase glass ceramics: the product consistency test (PCT ) method specified in. The sample was pulverized and sieved to separate a powder with a particle size fraction of 100 to 200 mesh, which was washed and dried to constant weight. 1.5 g of each sample was placed in a teflon container filled with deionized water. After sealing, put it in an oven at 90°C for 7 days. Use ICP-OES to measure the concentration of various elements in the leach solution, and evaluate the chemical stability by calculating the normalized mass loss of each element. As shown in Figure 4, the normalized leaching rate of each element is far below 1 gram /( m2 ·day), which meets the requirements of performance evaluation of solidified nuclear waste and is suitable for long-term underground geological storage.
实施例2:Example 2:
按照表1中实施例2称取磷酸二氢铵64.8克、三氧化二铁15克、氧化铝14克、碳酸锂2.5克、氧化镁1克、碳酸钡16.5克、碳酸钾18.4克,氧化铋2克、氧化硅0.5克、氧化铬1克,混合均匀,得到混合料。在1200℃的电熔炉中熔化后,通入氧气2小时,气量为120升/小时,得到澄清均匀的玻璃熔体。将澄清均匀的玻璃熔体浇注在通入冷却水的中空不锈钢辊筒上,压制成3mm厚的玻璃片,然后机器粉碎,得到外径1-3mm大小的玻璃块体。把玻璃碎块与石墨粉体按照质量比1:1的比例混合,转移到一个摇摆式电熔炉中,温度设为950℃,摇摆频率为30转/分钟,摇摆角度120°,快速摇摆20分钟,使玻璃块迅速表面软化,并且在表面张力的作用下棱角收缩,随着炉子的摇摆滚动形成玻璃球。转移玻璃球及石墨粉的混合物至480℃的退火炉中,退火4小时。然后随炉冷却至室温,过筛,筛出石墨粉,得到直径小于3mm、大于1mm的玻璃珠。把过筛的玻璃珠投入浓度均为0.3mol/L的Na2CO3/NaOH溶液中,搅拌10~15分钟,使碱液与玻璃珠表面反应,以快速去除玻璃珠表面的石墨粉,再用清水、酒精、去离子水依次冲洗玻璃珠表面的碱液,最后转移到90℃烘箱中烘干,得到铁磷酸盐玻璃珠。According to Example 2 in Table 1, take by weighing 64.8 grams of ammonium dihydrogen phosphate, 15 grams of ferric oxide, 14 grams of aluminum oxide, 2.5 grams of lithium carbonate, 1 gram of magnesium oxide, 16.5 grams of barium carbonate, 18.4 grams of potassium carbonate, bismuth oxide 2 grams, 0.5 grams of silicon oxide, and 1 gram of chromium oxide were uniformly mixed to obtain a mixture. After melting in an electric melting furnace at 1200°C, oxygen was introduced for 2 hours at a gas volume of 120 liters/hour to obtain a clear and uniform glass melt. The clarified and uniform glass melt is poured on a hollow stainless steel roller fed with cooling water, pressed into a 3mm thick glass sheet, and then crushed by a machine to obtain a glass block with an outer diameter of 1-3mm. Mix glass pieces and graphite powder according to the mass ratio of 1:1, transfer to a swing electric melting furnace, set the temperature at 950°C, swing frequency at 30 rpm, swing angle at 120°, and swing quickly for 20 minutes , so that the surface of the glass block is softened rapidly, and the edges and corners shrink under the action of surface tension, and the glass ball is formed as the furnace swings and rolls. Transfer the mixture of glass spheres and graphite powder to an annealing furnace at 480° C., and anneal for 4 hours. Then cool down to room temperature with the furnace, sieve, and sieve out the graphite powder to obtain glass beads with a diameter less than 3 mm and greater than 1 mm. Put the sieved glass beads into the Na 2 CO 3 /NaOH solution with a concentration of 0.3mol/L, and stir for 10-15 minutes to make the lye react with the surface of the glass beads to quickly remove the graphite powder on the surface of the glass beads, and then Rinse the lye on the surface of the glass beads sequentially with water, alcohol, and deionized water, and finally transfer to an oven at 90°C for drying to obtain iron phosphate glass beads.
实施例3:Example 3:
按照表1中实施例3称取五氧化二磷41克、三氧化二铁5克、氧化铝20克、碳酸钠25.6克、碳酸锶21.4克、氧化铋1克、氧化硅2克、氧化铬1克,混合均匀,得到混合料,在1200℃的电熔炉中熔化后,通入氧气2小时,气量为100升/小时,得到澄清均匀的玻璃熔体。将澄清均匀的玻璃熔体浇注在通入冷却水的中空不锈钢辊筒上,压制成3mm厚的玻璃片,然后机器粉碎,得到外径1-3mm大小的玻璃块体。把玻璃碎块与石墨粉体按照质量比1:1的比例混合,转移到一个摇摆式电熔炉中,温度设为920℃,摇摆频率为30转/分钟,摇摆角度120°,快速摇摆20分钟,使玻璃块迅速表面软化,并且在表面张力的作用下棱角收缩,随着炉子的摇摆滚动形成玻璃球。转移玻璃球及石墨粉的混合物至480℃的退火炉中,退火4小时。然后随炉冷却至室温,过筛,筛出石墨粉,得到直径小于3mm、大于1mm的玻璃珠。把过筛的玻璃珠投入浓度均为0.3mol/L的Na2CO3/NaOH溶液中,搅拌10~15分钟,使碱液与玻璃珠表面反应,以快速去除玻璃珠表面的石墨粉,再用清水、酒精、去离子水依次冲洗玻璃珠表面的碱液,最后转移到90℃烘箱中烘干,得到铁磷酸盐玻璃珠。Take by weighing 41 grams of phosphorus pentoxide, 5 grams of ferric oxide, 20 grams of aluminum oxide, 25.6 grams of sodium carbonate, 21.4 grams of strontium carbonate, 1 gram of bismuth oxide, 2 grams of silicon oxide, and chromium oxide according to Example 3 in Table 1. 1 g, mixed evenly to obtain a mixture, which was melted in an electric melting furnace at 1200° C., and then fed with oxygen for 2 hours at a rate of 100 liters/hour to obtain a clear and uniform glass melt. The clarified and uniform glass melt is poured on a hollow stainless steel roller fed with cooling water, pressed into a 3mm thick glass sheet, and then crushed by a machine to obtain a glass block with an outer diameter of 1-3mm. Mix glass pieces and graphite powder in a mass ratio of 1:1, transfer to a swing-type electric melting furnace, set the temperature at 920°C, swing frequency at 30 rpm, swing angle at 120°, and swing quickly for 20 minutes , so that the surface of the glass block is softened rapidly, and the edges and corners shrink under the action of surface tension, and the glass ball is formed as the furnace swings and rolls. Transfer the mixture of glass spheres and graphite powder to an annealing furnace at 480° C., and anneal for 4 hours. Then cool down to room temperature with the furnace, sieve, and sieve out the graphite powder to obtain glass beads with a diameter less than 3 mm and greater than 1 mm. Put the sieved glass beads into the Na 2 CO 3 /NaOH solution with a concentration of 0.3mol/L, and stir for 10-15 minutes to make the lye react with the surface of the glass beads to quickly remove the graphite powder on the surface of the glass beads, and then Rinse the lye on the surface of the glass beads sequentially with water, alcohol, and deionized water, and finally transfer to an oven at 90°C for drying to obtain iron phosphate glass beads.
实施例4:Example 4:
按照表1中实施例4称取五氧化二磷70克、三氧化二铁7克、氧化铝10克、碳酸钠13.7克、氧化铋2克、氧化硅2克、氧化铬1克,混合均匀,得到混合料,在1100℃的电熔炉中熔化后,通入氧气2小时,气量为100升/小时,得到澄清均匀的玻璃熔体。将澄清均匀的玻璃熔体浇注在通入冷却水的中空不锈钢辊筒上,压制成3mm厚的玻璃片,然后机器粉碎,得到外径1-3mm大小的玻璃块体。把玻璃碎块与石墨粉体按照质量比1:1的比例混合,转移到一个摇摆式电熔炉中,温度设为850℃,摇摆频率为30转/分钟,摇摆角度120°,快速摇摆20分钟,使玻璃块迅速表面软化,并且在表面张力的作用下棱角收缩,随着炉子的摇摆滚动形成玻璃球。转移玻璃球及石墨粉的混合物至450℃的退火炉中,退火4小时。然后随炉冷却至室温,过筛,筛出石墨粉,得到直径小于3mm、大于1mm的玻璃珠。把过筛的玻璃珠投入浓度均为0.3mol/L的Na2CO3/NaOH溶液中,搅拌10~15分钟,使碱液与玻璃珠表面反应,以快速去除玻璃珠表面的石墨粉,再用清水、酒精、去离子水依次冲洗玻璃珠表面的碱液,最后转移到90℃烘箱中烘干,得到铁磷酸盐玻璃珠。Take by weighing 70 grams of phosphorus pentoxide, 7 grams of ferric oxide, 10 grams of aluminum oxide, 13.7 grams of sodium carbonate, 2 grams of bismuth oxide, 2 grams of silicon oxide, and 1 gram of chromium oxide according to Example 4 in Table 1, and mix well , to obtain the mixture, which was melted in an electric melting furnace at 1100°C, and then fed with oxygen for 2 hours, with a gas volume of 100 liters/hour, to obtain a clear and uniform glass melt. The clarified and uniform glass melt is poured on a hollow stainless steel roller fed with cooling water, pressed into a 3mm thick glass sheet, and then crushed by a machine to obtain a glass block with an outer diameter of 1-3mm. Mix glass pieces and graphite powder in a mass ratio of 1:1, transfer to a swing electric furnace, set the temperature to 850°C, swing frequency to 30 rpm, swing angle to 120°, and swing quickly for 20 minutes , so that the surface of the glass block is softened rapidly, and the edges and corners shrink under the action of surface tension, and the glass ball is formed as the furnace swings and rolls. Transfer the mixture of glass spheres and graphite powder to an annealing furnace at 450° C., and anneal for 4 hours. Then cool down to room temperature with the furnace, sieve, and sieve out the graphite powder to obtain glass beads with a diameter less than 3 mm and greater than 1 mm. Put the sieved glass beads into the Na 2 CO 3 /NaOH solution with a concentration of 0.3mol/L, and stir for 10-15 minutes to make the lye react with the surface of the glass beads to quickly remove the graphite powder on the surface of the glass beads, and then Rinse the lye on the surface of the glass beads sequentially with water, alcohol, and deionized water, and finally transfer to an oven at 90°C for drying to obtain iron phosphate glass beads.
实施例5:Example 5:
按照表1中实施例5称取磷酸二氢铵78克、三氧化二铁5克、氧化铝30克、碳酸钠17.1克、碳酸钙6.25克、氧化铋0.5克、氧化硅1克、氧化铬2克,混合均匀,得到混合料,在1150℃的电熔炉中熔化后,通入氧气2小时,气量为120升/小时,得到澄清均匀的玻璃熔体。将澄清均匀的玻璃熔体浇注在通入冷却水的中空不锈钢辊筒上,压制成3mm厚的玻璃片,然后机器粉碎,得到外径1-3mm大小的玻璃块体。把玻璃碎块与石墨粉体按照质量比1:1的比例混合,转移到一个摇摆式电熔炉中,温度设为900℃,摇摆频率为30转/分钟,摇摆角度120°,快速摇摆20分钟,使玻璃块迅速表面软化,并且在表面张力的作用下棱角收缩,随着炉子的摇摆滚动形成玻璃球。转移玻璃球及石墨粉的混合物至470℃的退火炉中,退火4小时。然后随炉冷却至室温,过筛,筛出石墨粉,得到直径小于3mm、大于1mm的玻璃珠。把过筛的玻璃珠投入浓度均为0.3mol/L的Na2CO3/NaOH溶液中,搅拌10~15分钟,使碱液与玻璃珠表面反应,以快速去除玻璃珠表面的石墨粉,再用清水、酒精、去离子水依次冲洗玻璃珠表面的碱液,最后转移到90℃烘箱中烘干,得到铁磷酸盐玻璃珠。Take by weighing 78 grams of ammonium dihydrogen phosphate, 5 grams of ferric oxide, 30 grams of aluminum oxide, 17.1 grams of sodium carbonate, 6.25 grams of calcium carbonate, 0.5 grams of bismuth oxide, 1 gram of silicon oxide, and chromium oxide according to Example 5 in Table 1. 2 g, mixed uniformly to obtain a mixture, which was melted in an electric melting furnace at 1150° C., and fed with oxygen for 2 hours at a rate of 120 liters/hour to obtain a clear and uniform glass melt. The clarified and uniform glass melt is poured on a hollow stainless steel roller fed with cooling water, pressed into a 3mm thick glass sheet, and then crushed by a machine to obtain a glass block with an outer diameter of 1-3mm. Mix glass pieces and graphite powder in a mass ratio of 1:1, transfer to a swing-type electric melting furnace, set the temperature to 900°C, swing frequency to 30 rpm, swing angle to 120°, and swing quickly for 20 minutes , so that the surface of the glass block is softened rapidly, and the edges and corners shrink under the action of surface tension, and the glass ball is formed as the furnace swings and rolls. Transfer the mixture of glass spheres and graphite powder to an annealing furnace at 470° C., and anneal for 4 hours. Then cool down to room temperature with the furnace, sieve, and sieve out the graphite powder to obtain glass beads with a diameter less than 3 mm and greater than 1 mm. Put the sieved glass beads into the Na 2 CO 3 /NaOH solution with a concentration of 0.3mol/L, and stir for 10-15 minutes to make the lye react with the surface of the glass beads to quickly remove the graphite powder on the surface of the glass beads, and then Rinse the lye on the surface of the glass beads sequentially with water, alcohol, and deionized water, and finally transfer to an oven at 90°C for drying to obtain iron phosphate glass beads.
本发明制备的铁磷酸盐玻璃珠包容性强,可以包容挥发性的放射性元素如锶、铯等元素,易析晶的锆、稀土元素,以及钼、硫等易产生黄相的元素。该方法制备的玻璃珠表面光滑,滚动性好,可方便的滚动加入固化玻璃焦耳陶瓷加热炉或电磁感应炉中连续熔炼,适合高放射性核废料的固化处理。The iron phosphate glass beads prepared by the invention have strong tolerance and can contain volatile radioactive elements such as strontium and cesium, zirconium and rare earth elements that are easy to devitrify, and elements that are easy to produce yellow phases such as molybdenum and sulfur. The glass beads prepared by the method have a smooth surface and good rolling property, and can be conveniently rolled into a solidified glass Joule ceramic heating furnace or an electromagnetic induction furnace for continuous melting, and are suitable for solidification treatment of high-radioactive nuclear waste.
Claims (7)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202211072009.4A CN115477474A (en) | 2022-09-02 | 2022-09-02 | Iron phosphate glass bead for radioactive nuclear waste solidification treatment and preparation method thereof |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202211072009.4A CN115477474A (en) | 2022-09-02 | 2022-09-02 | Iron phosphate glass bead for radioactive nuclear waste solidification treatment and preparation method thereof |
Publications (1)
Publication Number | Publication Date |
---|---|
CN115477474A true CN115477474A (en) | 2022-12-16 |
Family
ID=84422265
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202211072009.4A Pending CN115477474A (en) | 2022-09-02 | 2022-09-02 | Iron phosphate glass bead for radioactive nuclear waste solidification treatment and preparation method thereof |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN115477474A (en) |
Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4847008A (en) * | 1984-04-11 | 1989-07-11 | The United States Of America As Represented By The Department Of Energy | Lead iron phosphate glass as a containment medium for disposal of high-level nuclear waste |
US5840638A (en) * | 1996-12-23 | 1998-11-24 | Brookhaven Science Associates | Phosphate glasses for radioactive, hazardous and mixed waste immobilization |
CN103547538A (en) * | 2011-05-25 | 2014-01-29 | 旭硝子株式会社 | Method for producing granules, method for producing molten glass, and method for producing glass articles |
CN103547541A (en) * | 2011-05-25 | 2014-01-29 | 旭硝子株式会社 | Granules, method for producing same, method for producing molten glass, and method for producing glass article |
CN105741897A (en) * | 2016-03-30 | 2016-07-06 | 中国科学院上海应用物理研究所 | Glass solidifying body for halide radioactive waste and preparation method thereof |
CN110078367A (en) * | 2019-04-22 | 2019-08-02 | 中国科学院上海光学精密机械研究所 | A kind of iron phosphorosilicate glass and preparation method thereof for the processing of level radioactive nuclear waste glass solidification |
CN114105472A (en) * | 2021-12-20 | 2022-03-01 | 中国科学院上海光学精密机械研究所 | Iron-containing high-phosphate glass, preparation method and application thereof |
CN114180834A (en) * | 2021-12-20 | 2022-03-15 | 中国科学院上海光学精密机械研究所 | Iron-containing low-phosphate glass, preparation method and application thereof |
CN114180833A (en) * | 2021-12-20 | 2022-03-15 | 中国科学院上海光学精密机械研究所 | Radioactive nuclear waste solidified iron phosphate glass with low corrosivity to alloy and preparation method thereof |
-
2022
- 2022-09-02 CN CN202211072009.4A patent/CN115477474A/en active Pending
Patent Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4847008A (en) * | 1984-04-11 | 1989-07-11 | The United States Of America As Represented By The Department Of Energy | Lead iron phosphate glass as a containment medium for disposal of high-level nuclear waste |
US5840638A (en) * | 1996-12-23 | 1998-11-24 | Brookhaven Science Associates | Phosphate glasses for radioactive, hazardous and mixed waste immobilization |
CN103547538A (en) * | 2011-05-25 | 2014-01-29 | 旭硝子株式会社 | Method for producing granules, method for producing molten glass, and method for producing glass articles |
CN103547541A (en) * | 2011-05-25 | 2014-01-29 | 旭硝子株式会社 | Granules, method for producing same, method for producing molten glass, and method for producing glass article |
CN105741897A (en) * | 2016-03-30 | 2016-07-06 | 中国科学院上海应用物理研究所 | Glass solidifying body for halide radioactive waste and preparation method thereof |
CN110078367A (en) * | 2019-04-22 | 2019-08-02 | 中国科学院上海光学精密机械研究所 | A kind of iron phosphorosilicate glass and preparation method thereof for the processing of level radioactive nuclear waste glass solidification |
CN114105472A (en) * | 2021-12-20 | 2022-03-01 | 中国科学院上海光学精密机械研究所 | Iron-containing high-phosphate glass, preparation method and application thereof |
CN114180834A (en) * | 2021-12-20 | 2022-03-15 | 中国科学院上海光学精密机械研究所 | Iron-containing low-phosphate glass, preparation method and application thereof |
CN114180833A (en) * | 2021-12-20 | 2022-03-15 | 中国科学院上海光学精密机械研究所 | Radioactive nuclear waste solidified iron phosphate glass with low corrosivity to alloy and preparation method thereof |
Non-Patent Citations (6)
Title |
---|
JEN-HSIEN HSU等: "The performance of Inconel 693 electrodes for processing an iron phosphate glass melt containing 26 wt.% of a simulated low activity waste", 《JOURNAL OF NUCLEAR MATERIALS》, vol. 444, pages 323, XP028785853, DOI: 10.1016/j.jnucmat.2013.09.055 * |
VESSELIN DIMITROV等: "Electronic oxide polarizability and optical basicity of simple oxides. I", 《JOURNAL OF APPLIED PHYSICS》, vol. 79, pages 1736 - 1740 * |
徐凯: "核废料玻璃固化国际研究进展", 《中国材料进展》, vol. 35, no. 7, pages 481 - 488 * |
朱敏: "《工程材料:数字资源版》", 31 August 2021, 冶金工业出版社, pages: 323 * |
西北轻工业学院编: "《玻璃工艺学》", 31 January 2000, 第23页, pages: 23 * |
金志浩等: "《工程陶瓷材料》", 30 September 1986, 机械工业出版社, pages: 19 * |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
US4514329A (en) | Process for vitrifying liquid radioactive waste | |
CN112624608B (en) | Borosilicate glass curing substrate and preparation method and application thereof | |
CN110970146A (en) | Borosilicate glass ceramic curing substrate and preparation method and application thereof | |
JPS6036999A (en) | Volume-reduction solidified body of radioactive sodium borate waste liquor, volume-reduction solidifying method anddevice thereof | |
JPWO2003024879A1 (en) | Waste glass recycling method and recycled glass | |
CN113754275A (en) | Radiation-proof glass | |
CN115583796B (en) | Glass solidified body for improving molybdenum element solubility and preparation method thereof | |
CN108417287B (en) | A method for co-processing waste lead-containing CRT glass and high-level waste liquid | |
Tong et al. | Structure and stability analysis of basaltic glasses for immobilizing simulated actinides nd, ce and La | |
CN115057618B (en) | Borosilicate solidified glass, preparation method and application thereof | |
CN104496190B (en) | A kind of thermal-state blast furnace slag mineral wool quenched material and preparation method thereof | |
CN115477474A (en) | Iron phosphate glass bead for radioactive nuclear waste solidification treatment and preparation method thereof | |
Li et al. | Preparation and characterization of glassy waste forms based on SrF2-Fe2O3-PbO/Bi2O3-P2O5 system | |
Tong et al. | Structure, crystallization behavior and chemical stability analysis of Nd3+-Basaltic glasses for immobilizing simulated trivalent actinides | |
CN117658460A (en) | Basic glass for solidifying high-level radioactive waste liquid, preparation method and application, and solidification method of high-level radioactive waste liquid | |
CN114180834B (en) | Iron-containing low-phosphate glass, preparation method and application thereof | |
CN114105472B (en) | Iron-containing high-phosphate glass, preparation method and application thereof | |
US5530174A (en) | Method of vitrifying high-level radioactive liquid waste | |
CN102167511A (en) | Manufacturing method of low-energy radiation protective glass | |
CN108314323A (en) | A kind of glass ceramic composite material preparation method containing pyrochlore | |
CN110335695A (en) | A kind of radioactive waste solidification base material and preparation method of glass solidification body | |
CN115050502A (en) | Glass curing treatment method for lead-bismuth alloy nuclear waste | |
JP2001027694A (en) | Solidified body of radioactive condensed waste substance and manufacture of the same | |
CN118420218B (en) | A glass substrate for solidifying high-calcium and high-titanium medium- and low-level radioactive waste ash, and its preparation method and application | |
CN111916246B (en) | Synergistic curing SrF 2 And glass solidified body of high-sodium high-iron waste material and preparation method thereof |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
RJ01 | Rejection of invention patent application after publication | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20221216 |