JP4364692B2 - Method for producing hydrogen concentrated water and hydrogen concentrated water - Google Patents
Method for producing hydrogen concentrated water and hydrogen concentrated water Download PDFInfo
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- JP4364692B2 JP4364692B2 JP2004092569A JP2004092569A JP4364692B2 JP 4364692 B2 JP4364692 B2 JP 4364692B2 JP 2004092569 A JP2004092569 A JP 2004092569A JP 2004092569 A JP2004092569 A JP 2004092569A JP 4364692 B2 JP4364692 B2 JP 4364692B2
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- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 title claims description 96
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims description 48
- 239000001257 hydrogen Substances 0.000 title claims description 39
- 229910052739 hydrogen Inorganic materials 0.000 title claims description 39
- 238000004519 manufacturing process Methods 0.000 title claims description 4
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 claims description 103
- 239000007864 aqueous solution Substances 0.000 claims description 55
- 229910052697 platinum Inorganic materials 0.000 claims description 43
- 238000006722 reduction reaction Methods 0.000 claims description 33
- 238000000034 method Methods 0.000 claims description 26
- 239000000243 solution Substances 0.000 claims description 21
- 239000010419 fine particle Substances 0.000 claims description 17
- 230000001603 reducing effect Effects 0.000 claims description 14
- 230000006911 nucleation Effects 0.000 claims description 7
- 238000010899 nucleation Methods 0.000 claims description 7
- 239000004094 surface-active agent Substances 0.000 claims description 7
- 239000003638 chemical reducing agent Substances 0.000 claims description 5
- 150000003057 platinum Chemical class 0.000 claims 1
- 229910052751 metal Inorganic materials 0.000 description 40
- 239000002184 metal Substances 0.000 description 40
- 239000011882 ultra-fine particle Substances 0.000 description 28
- 230000002829 reductive effect Effects 0.000 description 27
- 239000000975 dye Substances 0.000 description 26
- CCBICDLNWJRFPO-UHFFFAOYSA-N 2,6-dichloroindophenol Chemical compound C1=CC(O)=CC=C1N=C1C=C(Cl)C(=O)C(Cl)=C1 CCBICDLNWJRFPO-UHFFFAOYSA-N 0.000 description 25
- 102100034289 Deoxynucleoside triphosphate triphosphohydrolase SAMHD1 Human genes 0.000 description 25
- 101000641031 Homo sapiens Deoxynucleoside triphosphate triphosphohydrolase SAMHD1 Proteins 0.000 description 25
- 238000006243 chemical reaction Methods 0.000 description 23
- 238000007664 blowing Methods 0.000 description 21
- 239000008213 purified water Substances 0.000 description 17
- KDLHZDBZIXYQEI-UHFFFAOYSA-N Palladium Chemical compound [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 description 14
- 150000003839 salts Chemical class 0.000 description 12
- 230000000694 effects Effects 0.000 description 11
- 239000007788 liquid Substances 0.000 description 11
- 230000000052 comparative effect Effects 0.000 description 10
- MGJZITXUQXWAKY-UHFFFAOYSA-N diphenyl-(2,4,6-trinitrophenyl)iminoazanium Chemical compound [O-][N+](=O)C1=CC([N+](=O)[O-])=CC([N+]([O-])=O)=C1N=[N+](C=1C=CC=CC=1)C1=CC=CC=C1 MGJZITXUQXWAKY-UHFFFAOYSA-N 0.000 description 10
- HHEAADYXPMHMCT-UHFFFAOYSA-N dpph Chemical compound [O-][N+](=O)C1=CC([N+](=O)[O-])=CC([N+]([O-])=O)=C1[N]N(C=1C=CC=CC=1)C1=CC=CC=C1 HHEAADYXPMHMCT-UHFFFAOYSA-N 0.000 description 10
- 238000005259 measurement Methods 0.000 description 10
- 239000002245 particle Substances 0.000 description 10
- 238000000746 purification Methods 0.000 description 10
- 239000012528 membrane Substances 0.000 description 9
- 238000000108 ultra-filtration Methods 0.000 description 9
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 8
- 230000002292 Radical scavenging effect Effects 0.000 description 8
- 239000000084 colloidal system Substances 0.000 description 8
- 238000004042 decolorization Methods 0.000 description 8
- 238000002347 injection Methods 0.000 description 8
- 239000007924 injection Substances 0.000 description 8
- 239000002923 metal particle Substances 0.000 description 8
- 238000003756 stirring Methods 0.000 description 8
- 238000010521 absorption reaction Methods 0.000 description 7
- 239000002253 acid Substances 0.000 description 7
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 7
- 239000001301 oxygen Substances 0.000 description 7
- 229910052760 oxygen Inorganic materials 0.000 description 7
- UIIMBOGNXHQVGW-UHFFFAOYSA-M Sodium bicarbonate Chemical compound [Na+].OC([O-])=O UIIMBOGNXHQVGW-UHFFFAOYSA-M 0.000 description 6
- 239000012141 concentrate Substances 0.000 description 6
- 238000001914 filtration Methods 0.000 description 6
- 229910052763 palladium Inorganic materials 0.000 description 6
- 239000000049 pigment Substances 0.000 description 6
- 239000003642 reactive oxygen metabolite Substances 0.000 description 6
- 230000002000 scavenging effect Effects 0.000 description 6
- 230000003647 oxidation Effects 0.000 description 5
- 238000007254 oxidation reaction Methods 0.000 description 5
- 238000005406 washing Methods 0.000 description 5
- 239000003963 antioxidant agent Substances 0.000 description 4
- 230000003078 antioxidant effect Effects 0.000 description 4
- -1 glycerin fatty acid ester Chemical class 0.000 description 4
- 229920000642 polymer Polymers 0.000 description 4
- YZCKVEUIGOORGS-UHFFFAOYSA-N Hydrogen atom Chemical compound [H] YZCKVEUIGOORGS-UHFFFAOYSA-N 0.000 description 3
- OUUQCZGPVNCOIJ-UHFFFAOYSA-M Superoxide Chemical compound [O-][O] OUUQCZGPVNCOIJ-UHFFFAOYSA-M 0.000 description 3
- 230000003197 catalytic effect Effects 0.000 description 3
- 239000012295 chemical reaction liquid Substances 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
- 230000008030 elimination Effects 0.000 description 3
- 238000003379 elimination reaction Methods 0.000 description 3
- 239000011521 glass Substances 0.000 description 3
- 150000002431 hydrogen Chemical class 0.000 description 3
- 229910021645 metal ion Inorganic materials 0.000 description 3
- 229910000030 sodium bicarbonate Inorganic materials 0.000 description 3
- 235000017557 sodium bicarbonate Nutrition 0.000 description 3
- 238000003860 storage Methods 0.000 description 3
- PEDCQBHIVMGVHV-UHFFFAOYSA-N Glycerol Natural products OCC(O)CO PEDCQBHIVMGVHV-UHFFFAOYSA-N 0.000 description 2
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 2
- 238000004140 cleaning Methods 0.000 description 2
- 235000014113 dietary fatty acids Nutrition 0.000 description 2
- 238000011156 evaluation Methods 0.000 description 2
- 238000002474 experimental method Methods 0.000 description 2
- 229930195729 fatty acid Natural products 0.000 description 2
- 239000000194 fatty acid Substances 0.000 description 2
- 235000011187 glycerol Nutrition 0.000 description 2
- FDGQSTZJBFJUBT-UHFFFAOYSA-N hypoxanthine Chemical compound O=C1NC=NC2=C1NC=N2 FDGQSTZJBFJUBT-UHFFFAOYSA-N 0.000 description 2
- 239000002105 nanoparticle Substances 0.000 description 2
- 238000012545 processing Methods 0.000 description 2
- 239000000047 product Substances 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 230000002441 reversible effect Effects 0.000 description 2
- 239000010948 rhodium Substances 0.000 description 2
- 229920006395 saturated elastomer Polymers 0.000 description 2
- 239000011550 stock solution Substances 0.000 description 2
- CVSUAFOWIXUYQA-UHFFFAOYSA-M 2,6-Dichlorophenolindophenol sodium salt Chemical compound [Na+].C1=CC([O-])=CC=C1N=C1C=C(Cl)C(=O)C(Cl)=C1 CVSUAFOWIXUYQA-UHFFFAOYSA-M 0.000 description 1
- UGQMRVRMYYASKQ-UHFFFAOYSA-N Hypoxanthine nucleoside Natural products OC1C(O)C(CO)OC1N1C(NC=NC2=O)=C2N=C1 UGQMRVRMYYASKQ-UHFFFAOYSA-N 0.000 description 1
- 102000004316 Oxidoreductases Human genes 0.000 description 1
- 108090000854 Oxidoreductases Proteins 0.000 description 1
- 101150003085 Pdcl gene Proteins 0.000 description 1
- KJTLSVCANCCWHF-UHFFFAOYSA-N Ruthenium Chemical compound [Ru] KJTLSVCANCCWHF-UHFFFAOYSA-N 0.000 description 1
- BQCADISMDOOEFD-UHFFFAOYSA-N Silver Chemical compound [Ag] BQCADISMDOOEFD-UHFFFAOYSA-N 0.000 description 1
- 230000003064 anti-oxidating effect Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000003054 catalyst Substances 0.000 description 1
- 238000010835 comparative analysis Methods 0.000 description 1
- 238000007872 degassing Methods 0.000 description 1
- 201000010099 disease Diseases 0.000 description 1
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 description 1
- BNIILDVGGAEEIG-UHFFFAOYSA-L disodium hydrogen phosphate Chemical compound [Na+].[Na+].OP([O-])([O-])=O BNIILDVGGAEEIG-UHFFFAOYSA-L 0.000 description 1
- 238000010494 dissociation reaction Methods 0.000 description 1
- 230000005593 dissociations Effects 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 239000002778 food additive Substances 0.000 description 1
- 235000013373 food additive Nutrition 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- PCHJSUWPFVWCPO-UHFFFAOYSA-N gold Chemical compound [Au] PCHJSUWPFVWCPO-UHFFFAOYSA-N 0.000 description 1
- 229910052737 gold Inorganic materials 0.000 description 1
- 239000010931 gold Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 229910052741 iridium Inorganic materials 0.000 description 1
- GKOZUEZYRPOHIO-UHFFFAOYSA-N iridium atom Chemical compound [Ir] GKOZUEZYRPOHIO-UHFFFAOYSA-N 0.000 description 1
- 230000031700 light absorption Effects 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 229910000510 noble metal Inorganic materials 0.000 description 1
- 150000002894 organic compounds Chemical class 0.000 description 1
- 229910052762 osmium Inorganic materials 0.000 description 1
- SYQBFIAQOQZEGI-UHFFFAOYSA-N osmium atom Chemical compound [Os] SYQBFIAQOQZEGI-UHFFFAOYSA-N 0.000 description 1
- 239000012466 permeate Substances 0.000 description 1
- 230000001376 precipitating effect Effects 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 230000035484 reaction time Effects 0.000 description 1
- 238000006479 redox reaction Methods 0.000 description 1
- 229910052703 rhodium Inorganic materials 0.000 description 1
- MHOVAHRLVXNVSD-UHFFFAOYSA-N rhodium atom Chemical compound [Rh] MHOVAHRLVXNVSD-UHFFFAOYSA-N 0.000 description 1
- 229910052707 ruthenium Inorganic materials 0.000 description 1
- 238000005070 sampling Methods 0.000 description 1
- 229910052709 silver Inorganic materials 0.000 description 1
- 239000004332 silver Substances 0.000 description 1
- WZWGGYFEOBVNLA-UHFFFAOYSA-N sodium;dihydrate Chemical compound O.O.[Na] WZWGGYFEOBVNLA-UHFFFAOYSA-N 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000003786 synthesis reaction Methods 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- 230000000007 visual effect Effects 0.000 description 1
- 229940088594 vitamin Drugs 0.000 description 1
- 229930003231 vitamin Natural products 0.000 description 1
- 238000005303 weighing Methods 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E60/00—Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
- Y02E60/30—Hydrogen technology
- Y02E60/32—Hydrogen storage
Landscapes
- Hydrogen, Water And Hydrids (AREA)
- Pharmaceuticals Containing Other Organic And Inorganic Compounds (AREA)
- Medicines Containing Material From Animals Or Micro-Organisms (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Description
この発明は、金属超微粒子に水素を吸蔵濃縮させることにより高濃度の水素濃縮方法及び高活性酸素種還元消去能または高抗酸化能を持つ水素濃縮水に関する。 The present invention relates to a high-concentration hydrogen concentration method and hydrogen-enriched water having a high-reactive oxygen species reduction-erasing ability or high anti-oxidation ability by absorbing and concentrating hydrogen in metal ultrafine particles.
白金、パラジウムなど白金族金属微粒子は著しく水素を吸蔵することは良く知られている。更に、水素吸蔵による還元力により、身体内で発生するスーパーオキシドアニオン(O2 −)、過酸化水素(H2O2)等の活性酸素種を消去する能力:SOD活性があることもよく知られている。特許文献1には、水に水素ガスを吹き込んで電解還元水を製造する方法が記載されている。特許文献2には、原料として使用されるものが食品添加物として認められたもので、水に界面活性剤としてのグリセリン脂肪酸エステルを添加した処理液を用いて、金属超微粒子含有水溶液を製造する方法が記載されている。 It is well known that platinum group metal particles such as platinum and palladium store hydrogen remarkably. Furthermore, it is well known that it has SOD activity: the ability to eliminate active oxygen species such as superoxide anion (O 2 − ) and hydrogen peroxide (H 2 O 2 ) generated in the body by the reducing power of hydrogen storage. It has been. Patent Document 1 describes a method for producing electrolytic reduced water by blowing hydrogen gas into water. In Patent Document 2, what is used as a raw material is recognized as a food additive, and an aqueous solution containing ultrafine metal particles is produced using a treatment liquid in which glycerin fatty acid ester as a surfactant is added to water. A method is described.
また、非特許文献1には、水を電気分解して陰極側に生成したアルカリイオン水又は電解還元水には、溶存水素が測定され、この水は身体に良い水と説明されている。また、非特許文献2には、電解水が活性水素を持つと言う仮説でSOD活性ありと説明している。これら活性酸素種還元消去能を増大させるには更に多くの水素を濃縮させる必要がある。
解決しようとする問題点は、電解還元水の活性酸素消去能を増大させるには更に多くの水素を濃縮させる必要があるが、電解還元水では水素を濃縮させることが難しいという点である。 The problem to be solved is that it is necessary to concentrate more hydrogen in order to increase the active oxygen scavenging ability of electrolytic reduced water, but it is difficult to concentrate hydrogen with electrolytic reduced water.
本発明は、白金族金属超微粒子含有水溶液中に含まれる白金族金属超微粒子に水素を吸蔵濃縮させて高活性酸素種還元消去能または高抗酸化能を持つ水素濃縮水を製造するものである。白金族金属超微粒子に水素を吸蔵濃縮させるには、白金族金属超微粒子含有水溶液内に水素ガスを任意に注入するが、注入の時期は、格別問題にはならない。例えば、金属塩還元反応処理前の水溶液中あるいは、金属塩還元反応処理開始後の水溶液中でも良いのはもちろんのこと、白金、パラジウムなど白金族金属超微粒子の核生成した時、さらには、反応終了時、生成した白金族金属超微粒子の洗浄精製後のいずれであってもよい。水素ガスの注入は、高圧の下で行なう方が水素吸蔵反応がより効率的で望ましい。 The present invention is to produce hydrogen-enriched water having high active oxygen species reduction and elimination ability or high antioxidant ability by absorbing and concentrating hydrogen in platinum group metal ultrafine particles contained in an aqueous solution containing ultrafine platinum group metals. . In order to occlude and concentrate hydrogen in the platinum group metal ultrafine particles, hydrogen gas is arbitrarily injected into the platinum group metal ultrafine particle-containing aqueous solution, but the timing of the injection is not a particular problem. For example, in the aqueous solution before the metal salt reduction reaction treatment or in the aqueous solution after the start of the metal salt reduction reaction treatment, of course, when the nucleation of platinum group metal ultrafine particles such as platinum and palladium is generated, the reaction is completed. At any time, it may be after washing and purification of the produced platinum group metal ultrafine particles. The injection of hydrogen gas is preferably performed under high pressure because the hydrogen storage reaction is more efficient.
白金族金属微粒子含有水溶液の還元力を酸化還元色素:DCIP色素(2,6ジクロロインドフェノールナトリウム二水和物)及びDPPH色素(1,1−ジフェニル−2−ピクリルヒドラジル)を用いて行った結果、水素を吸蔵した本発明による水素濃縮水は、元の白金族金属微粒子含有水溶液に比べて、これらの色素を瞬時に酸化型から還元型に変えて、還元力が大幅に向上することが確認できた。その結果、活性酸素種消去能および抗酸化能を大幅に向上することができた。 The reducing power of an aqueous solution containing platinum group metal fine particles is measured using a redox dye: DCIP dye (2,6 dichloroindophenol sodium dihydrate) and DPPH dye (1,1-diphenyl-2-picrylhydrazyl). As a result, the hydrogen-enriched water according to the present invention, which occludes hydrogen, instantly changes these dyes from the oxidized form to the reduced form and greatly improves the reducing power compared to the original aqueous solution containing platinum group metal particles Was confirmed. As a result, the reactive oxygen species scavenging ability and antioxidant ability could be greatly improved.
本発明は、金属塩還元反応処理と、水素ガスの注入処理を行なうものである。金属塩還元反応処理は、白金族金属の塩を水溶液中で界面活性剤やポリマー等の高分子の存在のもとで還元処理することによって白金族金属微粒子を生成させる処理であり、水素ガスの注入処理は、金属塩還元反応処理前の水溶液又は金属塩還元反応処理によって生成した白金族金属超微粒子含有水溶液内に水素ガスを任意に注入して金属超微粒子に水素を吸蔵濃縮させる処理である。金属塩還元反応処理は、さらに金属微粒子を析出させる還元反応処理と、これら生成された金属微粒子をろ過して精製水で洗浄する精製処理とから構成される。 The present invention performs a metal salt reduction reaction process and a hydrogen gas injection process. The metal salt reduction reaction treatment is a treatment for producing platinum group metal fine particles by reducing a platinum group metal salt in an aqueous solution in the presence of a polymer such as a surfactant or a polymer. The injection process is a process in which hydrogen gas is arbitrarily injected into the aqueous solution containing the platinum group metal ultrafine particles generated by the aqueous solution before the metal salt reduction reaction treatment or the metal salt reduction reaction treatment, and hydrogen is occluded and concentrated in the metal ultrafine particles. . The metal salt reduction reaction treatment further includes a reduction reaction treatment for precipitating metal fine particles and a purification treatment for filtering the generated metal fine particles and washing with purified water.
還元反応処理は、さらに原料となる塩化白金酸(H2PtCl6)等の金属塩、反応液としてのエタノール(CH3CH2OH)等の還元剤、炭酸水素ナトリウム(NaHCO3)等のpH補償剤、生成した金属コロイドを安定的に分散させるための界面活性剤やポリマー等の高分子、反応に使用する精製水を計量する秤量処理と、これら反応液を攪拌しながら加熱昇温して反応する反応処理とからなる。 The reduction reaction treatment further includes a metal salt such as chloroplatinic acid (H 2 PtCl 6 ) as a raw material, a reducing agent such as ethanol (CH 3 CH 2 OH) as a reaction solution, and a pH such as sodium hydrogen carbonate (NaHCO 3 ). Weighing process to weigh the compensator, polymer such as surfactant and polymer to stably disperse the generated metal colloid, purified water used in the reaction, and heat the reaction liquid while stirring It consists of a reaction process that reacts.
水素ガスの注入処理については、白金族金属超微粒子含有水溶液内に水素ガスを任意に注入することができるが、還元反応処理での水素ガス吹込みは還元反応処理の反応開始時から吹込む方法と反応液の色調が変化を始める核生成後から吹込む方法と反応終了後から吹込む方法が考えられる。次に精製処理で水素ガスを吹込む方法としては、限外ろ過膜にて濃縮・洗浄する時の濃縮液側に水素ガスを吹込む方法がある。もう一つの方法は、精製処理が完了した完成品としての金属超微粒子含有水溶液に水素ガスを吹込む方法等が考えられる。 As for the hydrogen gas injection treatment, hydrogen gas can be arbitrarily injected into the aqueous solution containing the platinum group metal ultrafine particles, but the hydrogen gas injection in the reduction reaction treatment is performed from the start of the reaction of the reduction reaction treatment. The method of blowing after the nucleation where the color of the reaction liquid starts to change and the method of blowing after the completion of the reaction are conceivable. Next, as a method of blowing hydrogen gas in the purification treatment, there is a method of blowing hydrogen gas to the concentrate side when concentrating and washing with an ultrafiltration membrane. Another method may be a method in which hydrogen gas is blown into an aqueous solution containing ultrafine metal particles as a finished product after the purification treatment is completed.
次に、水素ガスの注入処理によって、金属超微粒子含有水溶液に水素が吸蔵・濃縮されたことを確認する方法として、水溶液を乾燥して真空・脱気して残存する水素を計る方法のほか、金属超微粒子含有水溶液即ち水溶液の状態での還元力を利用するため、溶存水素計による溶存水素量測定法、酸化・還元反応での還元反応による活性酸素種消去能および抗酸化能を評価する酸化還元色素で酸化・還元反応を可逆的に繰り返してDCIP(2,6−Dichlorindophenol Sodium Salt Dihydrate)色素による還元力を見る方法とDPPHラジカルの酸化型ラジカルを消去する一方的な還元力を調べるDPPH(1,1−Diphenyl−2−picrylhydrazyl)色素法及びスーパーオキシドアニオン(O2 −)消去活性に用いられるHPX−XOD系(ヒポキサンチン−キサンチン酸化酵素系)等で比較評価する方法があるが、本発明においては、DPPHラジカルでのラジカル消去還元力で当り実験を行い、DCIP色素による還元力で評価した。 Next, as a method of confirming that hydrogen has been occluded and concentrated in the aqueous solution containing metal ultrafine particles by hydrogen gas injection treatment, in addition to a method of measuring the remaining hydrogen by drying and vacuuming / degassing the aqueous solution, In order to utilize the reducing power in the aqueous solution containing metal ultrafine particles, that is, in the state of aqueous solution, the method for measuring the amount of dissolved hydrogen with a dissolved hydrogen meter, oxidation for evaluating reactive oxygen species scavenging ability and antioxidant ability by reduction reaction in oxidation / reduction reaction Reversible and reversible oxidation / reduction reactions with reducing dyes to observe the reducing power of DCIP (2,6-Dichlorindophenol Sodium Salt Dihydrate) dyes and DPPH ( 1,1-Diphenyl-2-picrylhydrazyl) dye method and superoxide anion (O 2 -) HPX-XOD system used in scavenging activity (hypoxanthine - hexa There is a method of comparative evaluation Chin oxidase system) or the like, in the present invention, performed per experiment radical scavenging reducing power in DPPH radical was evaluated by reducing power by DCIP dye.
評価に際しては、まずDCIP色素評価原液として(1)DCIP0.05grをエタノール70mlに溶解(2)1mlを採取してエタノール24mlへ注入(3)5mlを採取して、リン酸水素二ナトリウム2.13mgを精製水180mlに溶解した溶液15mlに注入し、これを原液とした。DCIP色素の酸化・還元反応を図1に示した。DPPHラジカルは図2に示す。図1に示す如く、酸化型DCIPは電子(e−)又は水素(H+)が供与されて還元脱色して還元型DCIPH2となる。従って、水素ガスを吹き込む本方式の場合、水素量に比例して還元速度は早くなる。換言すれば、還元脱色時間は水素量に比例すると言える。 In the evaluation, first, as DCIP dye evaluation stock solution, (1) 0.05 g DCIP was dissolved in 70 ml ethanol (2) 1 ml was collected and injected into 24 ml ethanol (3) 5 ml was collected to obtain 2.13 mg disodium hydrogen phosphate Was poured into 15 ml of a solution dissolved in 180 ml of purified water to make a stock solution. The oxidation / reduction reaction of the DCIP dye is shown in FIG. The DPPH radical is shown in FIG. As shown in FIG. 1, oxidized DCIP is supplied with electrons (e − ) or hydrogen (H + ), and is reduced and decolored to form reduced DCIPH 2 . Therefore, in the case of this method in which hydrogen gas is blown, the reduction rate increases in proportion to the amount of hydrogen. In other words, it can be said that the reductive decolorization time is proportional to the amount of hydrogen.
又、図2に示す如く、酸化型DPPHラジカルは電子(e−)又は水素(H+)によりラジカル消去が行われ、還元脱色して還元型DPPHとなる。前記DCIP同様、還元脱色時間は水素量に比例することになる。 Further, as shown in FIG. 2, the oxidized DPPH radical is radical-erased by electrons (e − ) or hydrogen (H + ), and is reduced and decolored to become reduced DPPH. Similar to the DCIP, the reductive decolorization time is proportional to the amount of hydrogen.
(実施例)
以下に本発明の実施例を説明する。
以下の実施例において、還元反応処理の反応中に水素ガスを吹込む場合に、反応開始から水素ガスを吹込むケース(1)と、金属微粒子核が生成を始める時点から水素ガスを吹込むケース(2)とが考えられる。その際、反応温度、攪拌回転数及び水素ガス量を変えた。結果は(1),(2)ともに攪拌回転数及び水素ガス量には前記DCIP及びDPPHの還元脱色時間にほとんど有意差は認められなかった。
(Example)
Examples of the present invention will be described below.
In the following examples, when hydrogen gas is blown during the reaction of the reduction reaction treatment, the case where hydrogen gas is blown from the start of the reaction (1) and the case where hydrogen gas is blown from the time when generation of metal fine particle nuclei starts. (2) is considered. At that time, the reaction temperature, the stirring speed and the amount of hydrogen gas were changed. As a result, in both (1) and (2), there was almost no significant difference in the reduction decoloration time of the DCIP and DPPH in the stirring rotation speed and the hydrogen gas amount.
従って、攪拌回転数及び水素ガス量は水素吸蔵量に有意差が認められなかったと言える。しかし、反応温度には、反応温度が高いほうが前記DCIP及びDPPHの還元脱色時間が早かった。従って、経済性を加味して、反応温度は通常の温度より若干高めにするのが望ましいと言える。また、金属微粒子核が生成を始める時期は、反応溶液の色が変化を始めるので、その色調変化を捉えて水素ガスを吹込む方法とした。 Therefore, it can be said that there was no significant difference in the amount of hydrogen occlusion between the stirring speed and the amount of hydrogen gas. However, the higher the reaction temperature, the faster the reductive decoloration time of the DCIP and DPPH. Therefore, it can be said that the reaction temperature is preferably slightly higher than the normal temperature in consideration of economy. In addition, since the color of the reaction solution began to change when the metal fine particle nuclei began to be generated, a method was adopted in which hydrogen gas was blown in by capturing the change in color tone.
次に、精製処理で水素ガスを吹込むには、限外ろ過膜にて濃縮・洗浄する時の濃縮液側に水素ガスを吹き込む場合で、濃縮・洗浄開始と同時に濃縮側に水素ガスを吹込むケース(3)と透過液側を塩分濃度測定器で塩分が不検出になってから更に10分間精製水で洗浄置換をするが、この10分間の洗浄置換の間だけ水素ガスの吹込むケース(4)とを行ったが、(3)と(4)には前記DCIP及びDPPHの還元脱色時間にほとんど有意差は認められなかった。 Next, in order to blow in hydrogen gas during the purification process, hydrogen gas is blown into the concentrate side when concentrating and washing with an ultrafiltration membrane. Case (3) and the permeate side are washed and replaced with purified water for an additional 10 minutes after no salinity is detected by a salinity meter, but hydrogen gas is blown in during this 10-minute washing and replacement. Although (4) was performed, almost no significant difference was recognized in the reductive decoloration time of the DCIP and DPPH in (3) and (4).
従って、(3)と(4)には水素吸蔵量に有意差が認められなかったと言える。経済性を加味して、限外ろ過膜での仕上げ洗浄の10分間の水素ガス吹込みとした。さらに、精製処理が完了した完成品としての金属超微粒子含有水溶液に水素ガスを吹込んだところ、前記記載限外ろ過膜での仕上げ洗浄と同様の結果が得られた。 Therefore, it can be said that there was no significant difference in hydrogen storage amount between (3) and (4). In consideration of economy, hydrogen gas was blown in for 10 minutes for final cleaning with an ultrafiltration membrane. Furthermore, when hydrogen gas was blown into the aqueous solution containing ultrafine metal particles as a finished product after the purification treatment was completed, the same results as in the above-described finish cleaning with the ultrafiltration membrane described above were obtained.
尚、前記水素ガス吹込み量はいずれの処理方法に於いても、処理対象水溶液量に対する水素の吹き込み量が1/100以下になるとDCIPの還元脱色時間が延びる傾向を示し、1/10以上ではDCIPの還元脱色時間に有意差が認められなかった。従って1/10以上では経済的に無駄になるので、処理対象水溶液量に対する水素の吹き込み量を1/100〜1/10に設定した。 Note that the hydrogen gas blowing amount shows a tendency for the DCIP reductive decoloration time to be extended when the hydrogen blowing amount with respect to the amount of the aqueous solution to be treated is 1/100 or less, and when it is 1/10 or more. There was no significant difference in DCIP reductive decolorization time. Therefore, since 1/10 or more is economically wasteful, the amount of hydrogen blown with respect to the amount of aqueous solution to be treated is set to 1/100 to 1/10.
本発明において、白金族元素としては、ルテニウム(Ru)、ロジウム(Rh)、パラジウム(Pd)、オスミウム(Os)、イリジウム(Ir)、白金(Pt)の6元素が良く知られ、いずれも水素吸蔵現象と考えられる挙動を示すが、特に工業的によく利用される白金(Pt)コロイド、パラジウム(Pd)コロイド含有水溶液がその水素吸蔵効果が優れていた。これら白金コロイド,パラジウムコロイドの粒子径は生成条件により1から20ナノメータ(nm)のものが得られた。 In the present invention, as the platinum group element, six elements of ruthenium (Ru), rhodium (Rh), palladium (Pd), osmium (Os), iridium (Ir), and platinum (Pt) are well known, all of which are hydrogen. Although the behavior considered to be an occlusion phenomenon is exhibited, an aqueous solution containing platinum (Pt) colloid or palladium (Pd) colloid, which is often used industrially, has an excellent hydrogen occlusion effect. The particle diameters of these platinum colloids and palladium colloids were 1 to 20 nanometers (nm) depending on the production conditions.
(実施例1)
A.金属塩還元反応処理と、水素ガスの注入処理とを以下の手順で行った。
(1)処理水の調製<水A>精製水を1μmの濾紙でろ過し、4500mlを準備した。
<還元剤B>エタノール(CH3CH2OH)を用い、これを450ml計量した。
<界面活性剤C>グリセリン脂肪酸エステルとして三菱化学フーズ製「L−10D」0.5gと理研ビタミン社製「J−0381V」1.5gを計量して混合した。
Example 1
A. The metal salt reduction reaction treatment and the hydrogen gas injection treatment were performed in the following procedure.
(1) Preparation of treated water <Water A> Purified water was filtered through a 1 μm filter paper to prepare 4500 ml.
<Reducing agent B> 450 ml of ethanol (CH 3 CH 2 OH) was weighed.
<Surfactant C> As a glycerin fatty acid ester, 0.5 g of “L-10D” manufactured by Mitsubishi Chemical Foods and 1.5 g of “J-0381V” manufactured by Riken Vitamin Co., Ltd. were weighed and mixed.
<金属イオン溶液D>塩化白金酸溶液(H2PtCl6)を準備し、この塩化白金酸溶液の5ml(Pt1g含有)を計量した。
<pH補償剤E>炭酸水素ナトリウム(NaHCO3)5gを準備し、ろ過した100mlの精製水にこの炭酸水素ナトリウム(NaHCO3)5gを溶解させた。
<水素ガス>高純度水素ガス(グレードG210L:純度(99.999%)ボンベで減圧弁、流量計を準備した。
<Metal ion solution D> A chloroplatinic acid solution (H 2 PtCl 6 ) was prepared, and 5 ml (containing Pt 1 g) of this chloroplatinic acid solution was weighed.
<PH compensator E> 5 g of sodium hydrogen carbonate (NaHCO 3 ) was prepared, and 5 g of this sodium hydrogen carbonate (NaHCO 3 ) was dissolved in 100 ml of purified water filtered.
<Hydrogen gas> A pressure reducing valve and a flow meter were prepared using a high purity hydrogen gas (grade G210L: purity (99.999%)) cylinder.
(2)還元処理上記水Aを処理液として容器にいれ、これを攪拌しながら温度を上げた。水の温度が60℃になった時点で水Aに上記還元剤Bと、界面活性剤Cとを添加した。還元剤Bと、界面活性剤Cとの添加後さらに、水Aを攪拌しながら温度を上げ、処理液の温度が70℃になった時点で金属イオン溶液DとpH補償剤Eとを同時に添加した。 (2) Reduction treatment The water A was put in a container as a treatment solution, and the temperature was raised while stirring the solution. When the temperature of the water reached 60 ° C., the reducing agent B and the surfactant C were added to the water A. After addition of reducing agent B and surfactant C, the temperature is increased while stirring water A, and metal ion solution D and pH compensator E are added simultaneously when the temperature of the treatment liquid reaches 70 ° C. did.
(3)温度を70℃に保持したまま、処理液の攪拌をつづけ、白金イオンが還元して核が生成し始めた時点は処理液の色調が変化を始める。その時点から水素ガスを400ml/minを処理液の下部より20分間吹込み、反応が終了した時点で攪拌および、加温を停止し、白金コロイドを得た。白金コロイド中の白金微粒子の粒子径は2〜3ナノメータ(nm)であった。 (3) The processing liquid is continuously stirred while the temperature is maintained at 70 ° C., and the color tone of the processing liquid starts to change when platinum ions are reduced and nuclei begin to be generated. From that time, 400 ml / min of hydrogen gas was blown in from the lower part of the treatment liquid for 20 minutes, and when the reaction was completed, stirring and heating were stopped to obtain a platinum colloid. The particle size of the platinum fine particles in the platinum colloid was 2 to 3 nanometers (nm).
(4)ろ過処理攪拌終了後の白金コロイドを1μmの濾紙でろ過し、12時間静置した。静置後、分画分子量10,000の限外ろ過膜で、精製水15,000mlを加えながらろ過を行い、白金超微粒子含有水溶液を得た。酸化還元色素実験に供したのは金属白金超微粒子含有水溶液である。得られた白金超微粒子含有水溶液の活性度を日立製吸光光度計(Spectrophotometer:U3210)を用いて試験した。 (4) Filtration treatment After completion of stirring, the platinum colloid was filtered through a 1 μm filter paper and allowed to stand for 12 hours. After standing, the mixture was filtered through an ultrafiltration membrane with a molecular weight cut-off of 10,000 while adding 15,000 ml of purified water to obtain an aqueous solution containing platinum ultrafine particles. An aqueous solution containing ultrafine metal platinum particles was used for the redox dye experiment. The activity of the obtained aqueous solution containing platinum ultrafine particles was tested using a Hitachi spectrophotometer (U3210).
(5)試験に際しては、まず、日立製吸光光度計の蓋付ガラスセルに酸化還元色素:DCIP試料3mlを注入して、更に前記白金超微粒子含有水溶液150μlを注入して、静かに5回振って吸光光度計にセットして、波長600nmで測定した。 (5) In the test, first, 3 ml of redox dye: DCIP sample was injected into a glass cell with a lid of Hitachi spectrophotometer, and then 150 μl of the aqueous solution containing platinum ultrafine particles was injected, and gently shaken 5 times. And set in an absorptiometer and measured at a wavelength of 600 nm.
B.結果の考察
測定結果を図3に示す。
(1)図3に示した如く、吸光強度(IO)が0.73から瞬時の0.18に変化脱色していることを示しており、さらに、測定溶液の入った測定用セルを5回程度振って空気中の酸素を処理液中に溶存させて酸化型DPICに戻して還元脱色の吸光強度(IO)の時間変化は前記初期のものと同様瞬時に還元脱色することが確認できた。更に、同様の酸化・還元を4回繰返したものを図3に示しているが、同様に瞬時に還元脱色している。結果、水素ガスを吹き込んで処理液中に生成した金属超微粒子含有水溶液は高活性を有し、しかも安定していることがわかった。
B. Discussion of results The measurement results are shown in FIG.
(1) As shown in FIG. 3, the absorption intensity (I O ) is changed from 0.73 to 0.18 instantaneously, and the measurement cell containing the measurement solution is set to 5 It can be confirmed that the oxygen concentration in the air is dissolved in the treatment liquid by shaking about once and returned to the oxidized DPIC, and the time change of the absorption intensity (I O ) of reductive decolorization is instantaneously reduced and decolorized in the same way as the initial one. It was. Further, FIG. 3 shows the same oxidation / reduction repeated four times. Similarly, the reduction and decolorization are instantaneously performed. As a result, it was found that the aqueous solution containing ultrafine metal particles produced in the treatment liquid by blowing hydrogen gas had high activity and was stable.
尚、水素ガスの吹込みを処理液の反応開始と同時に行ったが、全く、前記吸光光度計での図3と同じパターンが得られた。従って、核生成時から水素ガス反応が寄与していると考えられる。更に、核生成時からの反応温度を75℃にしたところ、さらに吸光強度(IO)の変化脱色が早くなった。 Although hydrogen gas was blown simultaneously with the start of the reaction of the treatment liquid, the same pattern as that in FIG. 3 was obtained using the absorptiometer. Therefore, it is considered that the hydrogen gas reaction has contributed from the time of nucleation. Furthermore, when the reaction temperature from the time of nucleation was increased to 75 ° C., the change and decolorization of the absorption intensity (I 2 O 3 ) was further accelerated.
(2)白金超微粒子含有水溶液の場合は、金属イオン溶液Dに塩化白金酸溶液(H2PtCl6)を準備し、この塩化白金酸溶液の5mlを計量して反応を行った。パラジウム超微粒子含有水溶液の場合は、塩化パラジウム酸溶液(H2Pdcl4)を準備し、この塩化パラジウム酸溶液5mlを計量して反応を行い、いずれの水素ガス処理で高活性を有することを確認した。その他金超微粒子含有水溶液及び銀超微粒子含有水溶液などの貴金属超微粒子含有水溶液も水素ガス処理で高活性になることが確認された。 (2) In the case of an aqueous solution containing platinum ultrafine particles, a chloroplatinic acid solution (H 2 PtCl 6 ) was prepared in the metal ion solution D, and 5 ml of this chloroplatinic acid solution was weighed and reacted. In the case of an aqueous solution containing palladium ultrafine particles, prepare a chloropalladium acid solution (H 2 Pdcl 4 ), measure 5 ml of this chloropalladium acid solution, and confirm that it has high activity in any hydrogen gas treatment. did. In addition, it was confirmed that aqueous solutions containing noble metal ultrafine particles such as an aqueous solution containing gold ultrafine particles and an aqueous solution containing silver ultrafine particles also became highly active by hydrogen gas treatment.
(比較例1)
前記実施例1での、水素ガス吹込みを行わずに、全く同じ反応を行って得られた金属白金超微粒子含有水溶液を、吸光光度計で全く同法で測定した結果を図4に示した。図4に示した如く、吸光強度(IO)が0.73から瞬時の0.18に変化脱色する時間が13分近くかかり、実施例1の水素ガスを吹き込んだものが瞬時に還元脱色したのに対し長時間を要している。更に、静かに5回振って測定すると約2.5分と短くなっているが、前記水素ガス吹込み試料が瞬時に還元脱色しているのに対して反応時間がかかっている。
(Comparative Example 1)
FIG. 4 shows the result of measuring the platinum metal ultrafine particle-containing aqueous solution obtained by carrying out the same reaction without blowing hydrogen gas in Example 1 with an absorptiometer in exactly the same manner. . As shown in FIG. 4, the absorption intensity (I O ) changed from 0.73 to 0.18 instantaneously and decolorization took nearly 13 minutes, and the hydrogen gas blown in Example 1 was instantaneously reduced and decolorized. It takes a long time. Furthermore, when measured by gently shaking 5 times, the measurement time is as short as about 2.5 minutes, but the reaction time is longer than that of the hydrogen gas blowing sample being instantaneously reduced and decolored.
初回の脱色変化は溶存酸素が飽和状態にあり、次回の静かに5回振ったものは、溶存酸素が飽和状態になっていなかった為還元脱色が早くなったと考えられる。 The first decoloration change is that the dissolved oxygen is in a saturated state, and the next one that was gently shaken five times is considered to have accelerated the reductive decoloration because the dissolved oxygen was not saturated.
(実施例2)
前記比較例1の反応終了液を精製処理において、反応液を1μmの定量濾紙でろ過し、12時間静置した。静置後、分画分子量10,000の限外ろ過膜で濾過する工程で、透過水中の塩分濃度が不検出になってから、金属白金超微粒子が濃縮された濃縮液側の下部から水素ガスを300ml/min吹き込む。その際使用する精製水は2,000mlで約20分加えながらろ過と水素吹込みを継続して、金属白金超微粒子含有水溶液を得た。
(Example 2)
In the purification treatment of the reaction completion liquid of Comparative Example 1, the reaction liquid was filtered through a 1 μm quantitative filter paper and allowed to stand for 12 hours. After standing, in the process of filtering through an ultrafiltration membrane with a molecular weight cut off of 10,000, hydrogen gas is introduced from the lower part of the concentrated liquid side where ultrafine metal platinum particles are concentrated after the salt concentration in the permeated water is not detected. Of 300 ml / min. Purified water used at that time was 2,000 ml for about 20 minutes, and filtration and hydrogen blowing were continued to obtain an aqueous solution containing ultrafine metal platinum particles.
実施例1と同様に、日立製吸光光度計(Spectrophotometer:U3210)の蓋付ガラスセルに酸化還元色素:DCIP試料3mlを注入して、更に前記金属超微粒子含有水溶液を150μlを注入して測定した。更に実施例1同様測定用セルを静かに5回振って吸光光度計にセットして、波長600nmで5回繰返して測定した。測定結果を図5に示す。図5に示した如く、実施例1同様に、吸光強度(IO)が0.73から瞬時に0.18まで還元脱色していることを示しており、処理液中に生成した金属白金超微粒子含有水溶液は高活性を有し、しかも安定していることがわかった。 In the same manner as in Example 1, 3 ml of redox dye: DCIP sample was injected into a glass cell with a lid of a Hitachi spectrophotometer (U3210), and 150 μl of the aqueous solution containing ultrafine metal particles was further injected. . Further, as in Example 1, the measurement cell was gently shaken 5 times and set in an absorptiometer, and measurement was repeated 5 times at a wavelength of 600 nm. The measurement results are shown in FIG. As shown in FIG. 5, as in Example 1, the absorption intensity (I 2 O 3 ) is reduced and decolorized from 0.73 to 0.18 instantaneously, and the amount of metallic platinum produced in the treatment liquid is higher. It was found that the aqueous solution containing fine particles had high activity and was stable.
(比較例2)
前記比較例1の反応終了液を精製工程において、反応液を1μmの定量濾紙でろ過し、12時間静置した。静置後、分画分子量10,000の限外ろ過膜で濾過する工程で、透過水中の塩分濃度が不検出になってから、水素ガスの吹き込みは行わず、更に、精製水2,000mlを約20分加えながらろ過を継続して、金属白金超微粒子含有水溶液を得た。その結果は、比較例1の図4に示した結果と同様であった。
(Comparative Example 2)
In the purification step, the reaction completed solution of Comparative Example 1 was filtered through a 1 μm quantitative filter paper and allowed to stand for 12 hours. After standing, in the step of filtering with an ultrafiltration membrane with a molecular weight cut off of 10,000, after the salt concentration in the permeated water is not detected, hydrogen gas is not blown, and 2,000 ml of purified water is further added. Filtration was continued while adding for about 20 minutes to obtain an aqueous solution containing ultrafine metal platinum particles. The result was the same as the result shown in FIG.
(実施例3)
比較例1での還元反応工程で生成した金属白金超微粒子含有水溶液を限外ろ過膜で濃縮・洗浄する精製工程を経たものを、白金濃度500ppmになるように調整した金属白金超微粒子含有水溶液を2,000ml準備する。水素ガス吹込み以前のものをコントロールとして、水素ガス300ml/minを本水溶液の下方から吹込み、1分後、3分後、10分後夫々150μlサンプリングして、実施例1と同様に、日立製吸光光度計(Spectrophotometer:U3210)の蓋付ガラスセルに酸化還元色素:DCIP試料3mlを注入して、更に前記サンプリング液夫々150μlを注入して、前記測定用セルを静かに5回振って吸光光度計にセットして、波長600nmで測定した。
(Example 3)
An aqueous solution containing ultrafine metal platinum particles adjusted to have a platinum concentration of 500 ppm is obtained by purifying an aqueous solution containing ultrafine metal platinum particles produced in the reduction reaction step in Comparative Example 1 using an ultrafiltration membrane. Prepare 2,000 ml. Hitachi gas 300 ml / min was blown from the bottom of the aqueous solution, and 150 μl was sampled after 1 minute, 3 minutes, and 10 minutes, respectively. Inject 3 ml of redox dye: DCIP sample into a glass cell with a lid of a spectrophotometer (U3210), inject 150 μl of each of the sampling solutions, and gently shake the measurement cell 5 times to absorb light. It set to the photometer and measured at wavelength 600nm.
測定結果を図6(a)〜(d)に示した。図6(a)は、コントロール、(b)はH2を1分間吹き込んだ場合、(c)はH2を3分間吹き込んだ場合、(d)はH2を10分間吹き込んだ場合である。結果は、実施例1及び実施例2で得られた結果と同じく、水素ガスを3分位の吹込みで充分な高活性が得られた。 The measurement results are shown in FIGS. FIG. 6A shows the control, FIG. 6B shows the case where H 2 was blown for 1 minute, FIG. 6C shows the case where H 2 was blown for 3 minutes, and FIG. 6D shows the case where H 2 was blown for 10 minutes. As a result, as in the results obtained in Example 1 and Example 2, sufficient high activity was obtained by blowing hydrogen gas into the third quantile.
次にDPPHラジカルのラジカル消去能についてDCIP色素と同様の測定を行った。コントロール及び水素ガス吹込み時間が1分後、3分後、10分後のサンプルを夫々20mlサンプリングして、10倍希釈したもの(1/10で表示)及び100倍希釈したもの(1/100で表示)を準備して、吸光光度計セルに50μMolのDPPHを2ml注入したセルに夫々注入して静かに5回程振って静置して脱色変化を目視と吸光光度計(波長:600nm)で測定した。夫々10分間経過後の吸光強度(IO)を表1及び図7に示した。表1には、下記比較例3と同様に、精製水2,000mlに水素ガス300ml/minを1分、3分及び10分間吹込んだもの、10分後のDPPH液のものも記載した。 Next, the radical scavenging ability of the DPPH radical was measured in the same manner as the DCIP dye. Samples of control and hydrogen gas blowing time after 1 minute, 3 minutes, and 10 minutes were each sampled in 20 ml, diluted 10 times (indicated by 1/10) and diluted 100 times (1/100) Display) and inject into 2 ml of 50 μMol of DPPH into the absorptiometer cell, gently shake it about 5 times and leave to stand to visually observe the decoloration change with a spectrophotometer (wavelength: 600 nm). It was measured. The absorption intensity (I O ) after 10 minutes is shown in Table 1 and FIG. In Table 1, as in Comparative Example 3 below, 300 ml / min of hydrogen gas was blown into 2,000 ml of purified water for 1 minute, 3 minutes, and 10 minutes, and the DPPH solution after 10 minutes was also listed.
(比較例3)
精製水2,000mlに水素ガス300ml/minを30分間吹込んだ精製水のDCIP色素の測定結果を図8に示した。
精製水に水素ガスを吹込んでも、酸化還元色素であるDCIP色素及びDPPHラジカル色素への還元反応は表2に示す如く、全く起こらないことが確認できた。
(Comparative Example 3)
FIG. 8 shows the measurement result of DCIP dye of purified water obtained by blowing hydrogen gas at 300 ml / min for 30 minutes into 2,000 ml of purified water.
It was confirmed that even when hydrogen gas was blown into purified water, the reduction reaction to DCIP dye and DPPH radical dye, which are redox dyes, did not occur at all as shown in Table 2.
表1には、DPPHラジカルの白金超微粒子含有水溶液の添加量と白金超微粒子含有水溶液への水素ガス吹き込み時間とによるラジカル消去能を波長(600nm)での吸光強度(IO)で示したものである。白金超微粒子含有水溶液の添加量としては、白金超微粒子含有水溶液を1/10に希釈したものを20μl、10μl、5μlと1/100の希釈したもの20μl、5μlをDPPH溶液に添加したものである。水素ガス吹き込み時間は、水素ガスを吹込まないものをコントロールとして、1分、3分、10分吹き込んだものとした。各測定値はDPPH液に添加して各10分経過後の吸光強度(IO)の値である。 Table 1 shows the radical scavenging ability in terms of the absorption intensity (I O ) at a wavelength (600 nm) depending on the amount of DPPH radical added in an aqueous solution containing platinum ultrafine particles and the time for blowing hydrogen gas into the aqueous solution containing platinum ultrafine particles. It is. As the addition amount of the aqueous solution containing platinum ultrafine particles, 20 μl, 10 μl, 5 μl and 1/100 diluted 20 μl, 5 μl of the diluted ultrafine platinum-containing aqueous solution are added to the DPPH solution. . The hydrogen gas blowing time was assumed to be blown for 1 minute, 3 minutes, and 10 minutes, with the hydrogen gas not blown as a control. Each measured value is the value of the light absorption intensity (I 2 O 3 ) after 10 minutes from the addition to the DPPH solution.
比較例として最下段に精製水のコントロール及び水素ガスを1分、3分、10分間吹き込んだものを列記した。精製水は水素ガスの吹き込み有無に関係なく、DPPHラジカル消去能がまったく無いことが確認できた。ラジカル消去能は水素ガス吹き込み時間、及び添加量に比例することが確認できた。 As a comparative example, the control of purified water and hydrogen gas blown in for 1 minute, 3 minutes, and 10 minutes are listed at the bottom. It was confirmed that purified water had no DPPH radical scavenging ability regardless of whether hydrogen gas was blown in or not. It was confirmed that the radical scavenging ability was proportional to the hydrogen gas blowing time and the amount added.
更に、表2にはDPPHラジカルの還元脱色で見られるラジカル消去能を目視で観察したもので、表1と同様に、白金微粒子含有水溶液添加量と水素ガス吹き込み時間とラジカル消去能が比例関係にあることを示している。又、精製水は水素ガス吹き込みに関係なくラジカル消去能が無いことが確認できた。 Further, Table 2 is a visual observation of the radical scavenging ability observed in the reductive decolorization of DPPH radicals. Like Table 1, the amount of platinum fine particle-containing aqueous solution added, hydrogen gas blowing time, and radical scavenging ability are in a proportional relationship. It shows that there is. Moreover, it was confirmed that purified water has no radical scavenging ability regardless of hydrogen gas blowing.
(実施例4)
比較例1での還元反応工程で生成した金属白金超微粒子含有水溶液を限外ろ過膜で濃縮・洗浄する精製工程を経たものを、白金濃度500ppmになるように調整した金属白金超微粒子含有水溶液を500ml準備して、1リットル圧力容器に注入して2Kg/cm2の圧力で100ml/minの吹込みで約2分で実施例3での10分処理と同等の高活性を得た。
(Example 4)
An aqueous solution containing ultrafine metal platinum particles adjusted to have a platinum concentration of 500 ppm is obtained by purifying an aqueous solution containing ultrafine metal platinum particles produced in the reduction reaction step in Comparative Example 1 using an ultrafiltration membrane. 500 ml was prepared, poured into a 1 liter pressure vessel, and a high activity equivalent to the 10 minute treatment in Example 3 was obtained in about 2 minutes by blowing with 100 ml / min at a pressure of 2 Kg / cm 2 .
更に2.5Kg/cm2及び3Kg/cm2と加圧したが、DCIPの還元脱色時間が2Kg/cm2の圧力のものと有意差が認められなかった。従って経済的観点から最大2Kg/cm2とした。 Further, pressurization was carried out at 2.5 kg / cm 2 and 3 kg / cm 2 , but no significant difference was observed from that with a DCIP reductive decoloration time of 2 kg / cm 2 . Therefore, the maximum is 2 Kg / cm 2 from the economical viewpoint.
これらの実施例の結果から、本来触媒能を有する金属白金微粒子はその周りの水分子H2Oをイオン解離(H+、OH−)して電気二重層を形成して電子(e−)又は水素(H+)供与型の還元性を持つと言われているが、図9に模式図で示した如く、ナノサイズ金属白金微粒子Pに水素H2が吸蔵されるため、表面エネルギーを増加させて、その結果、還元力が向上すると推測される。さらに吸蔵された水素が、金属白金微粒子の触媒能により活性水素化されて還元力が向上したとも考えられる。 From the results of these examples, the platinum metal particles originally having catalytic ability form an electric double layer by ion dissociation (H + , OH − ) of the surrounding water molecules H 2 O to form electrons (e − ) or Although it is said that it has hydrogen (H + ) donating-type reducing properties, as shown in the schematic diagram of FIG. 9, since hydrogen H 2 is occluded in the nano-sized metal platinum fine particles P, the surface energy is increased. As a result, it is estimated that the reducing power is improved. Furthermore, it is considered that the stored hydrogen is activated hydrogenated by the catalytic ability of the metal platinum fine particles, and the reducing power is improved.
身体内で発生するスーパーオキシドアニオン(O2 −)、過酸化水素(H2O2)等の活性酸素種による疾患を、活性酸素種消去能や抗酸化能による改善効果を利用する医療分野をはじめ、高活性触媒能を利用する有機化合物合成などの触媒分野へ利用できる。 In the medical field that utilizes the improvement effect of reactive oxygen species scavenging ability and antioxidant ability on diseases caused by reactive oxygen species such as superoxide anion (O 2 − ) and hydrogen peroxide (H 2 O 2 ) generated in the body First, it can be used in the field of catalysts such as organic compound synthesis utilizing high activity catalytic ability.
P ナノサイズ白金微粒子
H2 水素
H+,OH― 水分子
P Nano-sized platinum fine particle H 2 Hydrogen H + , OH - Water molecule
Claims (4)
白金の塩を水溶液中で還元することにより白金微粒子を生成させる工程を含み、
該工程において還元反応中の水溶液に水素ガスを注入することを特徴とする方法。 A method for producing hydrogen-enriched water containing platinum fine particles ,
Including a step of generating platinum fine particles by reducing a platinum salt in an aqueous solution ,
A method comprising injecting hydrogen gas into an aqueous solution during the reduction reaction in the step .
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